【注意事項】
* 化学物質有害性情報データベース情報更新日が2019年9月以前はRead-acrossデータでも○としていないので、毒性値の取り扱いには注意が必要である。
| 生物種 | 学名 | 影響内容 | エンドポイント | 暴露期間(値) | 暴露期間(単位) | 毒性値 | 毒性値(単位) | Read-across * | QSAR | GLP | 設定濃度 | 実測濃度 | 情報源 | 情報源による信頼性評価 | 著者 | タイトル | 記載誌 | 発行年 | 情報更新日 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| subject type | scientific name | effect | endpoint | exposure duration value | exposure duration unit | toxicity value | toxicity unit | Read-across | QSAR | GLP | nominal concentration | measured concentration | original work type | original work reliability rank | author | title | referenced journal | publication year | Information update date |
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass, the growth rate, the pigment diversity , the autotrophic index | an optimal concentration range | 1～35 | μg/L [Cu] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||||
| 藻類 | Anabaena lemmermannii | growth | EC100 | days | 0.25 | μmol/L | 16 ECOTOX | Luderitz,V., and A. Nicklisch | Response of Phytoplankton to Copper Treatment with Reference to Species Sensitivity | Int. Rev. Gesamten Hydrobiol.74(6): 657-668 | 1989 | 2022/01/25 | |||||||
| 藻類 | Anabaena solitaria | growth | EC100 | days | 0.8 | μmol/L | 16 ECOTOX | Luderitz,V., and A. Nicklisch | Response of Phytoplankton to Copper Treatment with Reference to Species Sensitivity | Int. Rev. Gesamten Hydrobiol.74(6): 657-668 | 1989 | 2022/01/25 | |||||||
| 藻類 | Chlorella vulgaris | cell number | LC25 | 6 | minutes | 0.7 | mg/L | 16 ECOTOX | Rai,P.K., and L.C. Rai | Interactive Effects of UV-B and Cu on Photosynthesis, Uptake and Metabolism of Nutrients in a Green Alga Chlorella vulgaris Under Simulated Ozone Column | J. Gen. Appl. Microbiol.43(5): 281-288 | 1997 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Biomass | IC25 | 24 | hours | 20.1 | μg/L | 16 ECOTOX | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2022/01/25 | ||||||
| 藻類 | Anabaena doliolum | Mortality | LD25 | 15 | days | 4.8 | μmol/L | 16 ECOTOX | Rai,L.C., B. Tyagi, P.K. Rai, and N. Mallick | Interactive Effects of UV-B and Heavy Metals (Cu and Pb) on Nitrogen and Phosphorus Metabolism of a N2-Fixing Cyanobacterium Anabaena doliolum | Environ. Exp. Bot.39(3): 221-231 | 1998 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Biomass | IC25 | 96 | hours | 8.1 | μg/L | 16 ECOTOX | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Mortality | NR-LETH | 7 | days | 300 | μg/L | 16 ECOTOX | Bartlett,L., F.W. Rabe, and W.H. Funk | Effects of Copper, Zinc and Cadmium on Selanastrum capricornutum | Water Res.8(3): 179-185 | 1974 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus quadricauda | growth | EC100 | days | 25 | μmol/L | 16 ECOTOX | Luderitz,V., and A. Nicklisch | Response of Phytoplankton to Copper Treatment with Reference to Species Sensitivity | Int. Rev. Gesamten Hydrobiol.74(6): 657-668 | 1989 | 2022/01/25 | |||||||
| 藻類 | Chlorella vulgaris | Physiology | LOEL | 2 | hours | 300000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mallick,N., and L.C. Rai | Metal Induced Inhibition of Photosynthesis, Photosynthetic Electron Transport Chain and ATP Content of Anabaena doliolum and Chlorella vulgaris: Interaction with Exogenous ATP | Biomed. Environ. Sci.5(3): 241-250 | 1992 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 4 | days | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Physiology | LOEL | 1 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEL | 1 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | LOEL | 15 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Accumulation | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Accumulation | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | LOEL | 15 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEL | 1 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Accumulation | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEL | 1 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Accumulation | LOEL | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | ||||||||
| 藻類 | Chlorella vulgaris | Physiology | LOEL | 1 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | NOEC | 4 | days | 100 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 63.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Accumulation | NOEC | 4 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 19.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | NOEC | 4 | days | 100 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 4 | days | 100 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | NOEC | 4 | days | 100 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Long-Term Acclimation of Pseudokirchneriella subcapitata (Korshikov) Hindak to Different Copper Concentrations: Changes in Tolerance and Physiology | Aquat. Toxicol.68(1): 61-74 | 2004 | 2016/03/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 3 | days | 64.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Physiology | LOEL | 1 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Physiology | LOEC | 1 | days | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 3 | days | 150 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | IC50 | 7 | days | 19.2 | その他others [umol/dm3] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kral'ova,K., K. Kissova, and O. Svajlenova | Effects of Carboxylatocopper(II) Complexes on Photosynthesizing Organisms | Chem. Inz. Ekol.7(10): 1076-1083 | 2000 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | IC50 | 7 | days | 14 | その他others [umol/dm3] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kral'ova,K., K. Kissova, and O. Svajlenova | Effects of Carboxylatocopper(II) Complexes on Photosynthesizing Organisms | Chem. Inz. Ekol.7(10): 1076-1083 | 2000 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | LC25 | 0.1 | hours | 700 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., and L.C. Rai | Interactive Effects of UV-B and Cu on Photosynthesis, Uptake and Metabolism of Nutrients in a Green Alga Chlorella vulgaris Under Simulated Ozone Column | J. Gen. Appl. Microbiol.43(5): 281-288 | 1997 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | LC50 | 0.25 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., and L.C. Rai | Interactive Effects of UV-B and Cu on Photosynthesis, Uptake and Metabolism of Nutrients in a Green Alga Chlorella vulgaris Under Simulated Ozone Column | J. Gen. Appl. Microbiol.43(5): 281-288 | 1997 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | LOEC | 4 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | LOEC | 1 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Physiology | LOEC | 4 | days | 150 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Accumulation | LOEC | 4 | days | 10 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | LOEC | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Long-Term Acclimation of Pseudokirchneriella subcapitata (Korshikov) Hindak to Different Copper Concentrations: Changes in Tolerance and Physiology | Aquat. Toxicol.68(1): 61-74 | 2004 | 2016/03/25 | ||||||||
| 藻類 | Chlorella vulgaris | Population | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | LOEC | 4.5 | hours | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Physiology | NOEC | 4 | hours | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | LOEC | 4.5 | hours | 52 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEC | 4.5 | hours | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Accumulation | LOEC | 2 | days | 63.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Accumulation | LOEC | 4 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEL | 1 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | LOEL | 3 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | |||||||
| 藻類 | Chlorella vulgaris | Accumulation | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEL | 2 | hours | 300000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mallick,N., and L.C. Rai | Metal Induced Inhibition of Photosynthesis, Photosynthetic Electron Transport Chain and ATP Content of Anabaena doliolum and Chlorella vulgaris: Interaction with Exogenous ATP | Biomed. Environ. Sci.5(3): 241-250 | 1992 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | LOEL | 2 | hours | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Physiology | LOEL | 1 | days | 2000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Physiology | LOEC | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Long-Term Acclimation of Pseudokirchneriella subcapitata (Korshikov) Hindak to Different Copper Concentrations: Changes in Tolerance and Physiology | Aquat. Toxicol.68(1): 61-74 | 2004 | 2016/03/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | Physiology | 4 | days | 500～1500 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cvetkovic,A.D., G. Samson, P. Couture, and R. Popovic | Study of Dependency Between Culture Growth and Photosynthetic Efficiency Measured by Fluorescence Induction in Selenastrum capricornutum Inhibited by Copper | Ecotoxicol. Environ. Saf.22:127-132 | 1991 | 2016/03/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | Physiology | NOEC | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Long-Term Acclimation of Pseudokirchneriella subcapitata (Korshikov) Hindak to Different Copper Concentrations: Changes in Tolerance and Physiology | Aquat. Toxicol.68(1): 61-74 | 2004 | 2016/03/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEL | 4 | days | 160 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEL | 3 | days | 33.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Mortality | 7 | days | 300 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bartlett,L., F.W. Rabe, and W.H. Funk | Effects of Copper, Zinc and Cadmium on Selanastrum capricornutum | Water Res.8(3): 179-185 | 1974 | 2016/03/25 | |||||||
| 藻類 | Chlorella vulgaris | Population | 4 | days | 2500～17500 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lam,P.K.S., P.F. Wut, A.C.W. Chan, and R.S.S. Wu | Individual and Combined Effects of Cadmium and Copper on the Growth Response of Chlorella vulgaris | Environ. Toxicol.14(3): 347-353 | 1999 | 2016/03/25 | ||||||||
| 藻類 | Chlorella vulgaris | Accumulation | 3 | days | 1000～30000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,L.C., and N. Mallick | Removal and Assessment of Toxicity of Cu and Fe to Anabaena doliolum and Chlorella vulgaris Using Free and Immobilized Cells | J. Microbiol. Biotechnol.8(2): 110-114 | 1992 | 2016/03/25 | ||||||||
| 藻類 | Chlorella vulgaris | Population | 1000～30000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,L.C., and N. Mallick | Removal and Assessment of Toxicity of Cu and Fe to Anabaena doliolum and Chlorella vulgaris Using Free and Immobilized Cells | J. Microbiol. Biotechnol.8(2): 110-114 | 1992 | 2016/03/25 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | 40～309 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Christensen,E.R., J. Scherfig, and P.S. Dixon | Effects of Manganese, Copper and Lead on Selenastrum capricornutum and Chlorella stigmatophora | Water Res.13(1): 79-92 | 1979 | 2016/03/25 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | 0.04～4000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Christensen,E.R., J. Scherfig, and P.S. Dixon | Effects of Manganese, Copper and Lead on Selenastrum capricornutum and Chlorella stigmatophora | Water Res.13(1): 79-92 | 1979 | 2016/03/25 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 170.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | 80～85 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Christensen,E.R., J. Scherfig, and P.S. Dixon | Effects of Manganese, Copper and Lead on Selenastrum capricornutum and Chlorella stigmatophora | Water Res.13(1): 79-92 | 1979 | 2016/03/25 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 57.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Cellular Effects | 33 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosko,J.J., and J.W. Rachlin | The Effect of Cadmium, Copper, Mercury, Zinc and Lead on Cell Division, Growth, and Chlorophyll A Content of the Chlorophyte Chlorella vulgaris | Bull. Torrey Bot. Club104(3): 226-233 | 1977 | 2016/03/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | 4 | days | 500～1500 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cvetkovic,A.D., G. Samson, P. Couture, and R. Popovic | Study of Dependency Between Culture Growth and Photosynthetic Efficiency Measured by Fluorescence Induction in Selenastrum capricornutum Inhibited by Copper | Ecotoxicol. Environ. Saf.22:127-132 | 1991 | 2016/03/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | 1 | days | 50 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sauser,K.R., K.T. Chung, and T.Y. Wong | Promutagen Activation by the Green Alga Selenastrum capricornutum | Environ. Toxicol. Chem.17(9): 1825-1829 | 1998 | 2016/03/25 | |||||||
| 藻類 | Chlorella vulgaris | Biochemical | 33 | days | 320 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosko,J.J., and J.W. Rachlin | The Effect of Cadmium, Copper, Mercury, Zinc and Lead on Cell Division, Growth, and Chlorophyll A Content of the Chlorophyte Chlorella vulgaris | Bull. Torrey Bot. Club104(3): 226-233 | 1977 | 2016/03/25 | |||||||
| 藻類 | Chlorella vulgaris | Biochemical | 1000～30000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rai,L.C., and N. Mallick | Removal and Assessment of Toxicity of Cu and Fe to Anabaena doliolum and Chlorella vulgaris Using Free and Immobilized Cells | J. Microbiol. Biotechnol.8(2): 110-114 | 1992 | 2016/03/25 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | 52～262 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | |||||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | 10～2000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van der Heever,J.A., and J.U. Grobbelaar | In Vivo Chlorophyll A Fluorescence of Selenastrum capricornutum as a Screening Bioassay in Toxicity Studies | Arch. Environ. Contam. Toxicol.35:281-286 | 1998 | 2016/03/25 | ||||||||||
| 藻類 | Chlorella vulgaris | Biochemical | 52～262 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | 8 | hours | 30 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kuwabara,J.S., and H.V. Leland | Adaptation of Selenastrum capricornutum (Chlorophyceae) to Copper | Environ. Toxicol. Chem.5(2): 197-203 | 1986 | 2016/03/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 53.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | 27 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Christensen,E.R., J. Scherfig, and P.S. Dixon | Effects of Manganese, Copper and Lead on Selenastrum capricornutum and Chlorella stigmatophora | Water Res.13(1): 79-92 | 1979 | 2016/03/25 | |||||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 49.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Physiology | NOEC | 1 | days | 52 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | NOEC | 4.5 | hours | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Physiology | NOEC | 1 | days | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | NOEC | 4 | days | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Biochemical | NOEC | 4.5 | hours | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Biochemical | NOEC | 4.5 | hours | 52 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Physiology | NOEC | 4 | hours | 262 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 53.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Accumulation | NOEC | 2 | days | 6.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 49.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 37.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 110.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 89.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 67.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 59.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 40.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 174 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 111.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 112.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 60.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 54.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 97.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 91.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 53.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 381.153 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atay,S., and H.B. Ozkoc | Effect of Sediment on the Bioavailability and Toxicity of Copper and Zinc to a Green Alga | Fresenius Environ. Bull.19(12a): 3018-3027 | 2010 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 154.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 68.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 61.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 53.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 15.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 66.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 18.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 4 | days | 4830 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lam,P.K.S., P.F. Wut, A.C.W. Chan, and R.S.S. Wu | Individual and Combined Effects of Cadmium and Copper on the Growth Response of Chlorella vulgaris | Environ. Toxicol.14(3): 347-353 | 1999 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 274.022 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atay,S., and H.B. Ozkoc | Effect of Sediment on the Bioavailability and Toxicity of Copper and Zinc to a Green Alga | Fresenius Environ. Bull.19(12a): 3018-3027 | 2010 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 179.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 146.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 311.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 33.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 26.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 215 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 19 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 341 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 145 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 453.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 142.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 127.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 168.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 103 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 121.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 96.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 3 | days | 147 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 91.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 43.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 46.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 92.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 16.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 42.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 14.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 56.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 89.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 75.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 55.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 42.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 55.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 59.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 25.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 118.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 43.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 93.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 52 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 94 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 148.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 134.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 105 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 127.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 105 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 171.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 104.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 316.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 60.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 88.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 113 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 65.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 3 | days | 16500 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Physiology | IC25 | 4 | days | 122.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 55 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Growth | EC50 | 3 | days | 7000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wren,M.J., and D. McCarroll | A Simple and Sensitive Bioassay for the Detection of Toxic Materials Using a Unicellular Green Alga | Environ. Pollut.64(1): 87-91 | 1990 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 4 | days | 200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Cellular Effects | EC50 | 33 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosko,J.J., and J.W. Rachlin | The Effect of Cadmium, Copper, Mercury, Zinc and Lead on Cell Division, Growth, and Chlorophyll A Content of the Chlorophyte Chlorella vulgaris | Bull. Torrey Bot. Club104(3): 226-233 | 1977 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 3 | days | 39900 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | IC10 | 4 | days | 5.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | IC25 | 1 | days | 20.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | IC25 | 4 | days | 8.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 198.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 175.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 3 | days | 280 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 4 | days | 72.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 356 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 30.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 490.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 178.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 66.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 130.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 134.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 160 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 12 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 285.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 138.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 234 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 51 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 37 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 3 | days | 7800 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 156.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 29.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 3 | days | 36500 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 3 | days | 38600 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 506.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 400 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 3 | days | 37300 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 3 | days | 35000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Population | EC50 | 3 | days | 34600 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 3 | days | 37 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Long-Term Acclimation of Pseudokirchneriella subcapitata (Korshikov) Hindak to Different Copper Concentrations: Changes in Tolerance and Physiology | Aquat. Toxicol.68(1): 61-74 | 2004 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Biochemical | LOEL | 7 | days | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Accumulation | LOEL | 6 | hours | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Biochemical | LOEL | 7 | days | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Accumulation | LOEL | 2 | days | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., and J.P. Gaur | Physiological Behavior of Scenedesmus sp. During Exposure to Elevated Levels of Cu and Zn and After Withdrawal of Metal Stress | Protoplasma229(1): 1-9 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Biochemical | LOEL | 6 | hours | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Physiology | LOEL | 2 | days | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., and J.P. Gaur | Physiological Behavior of Scenedesmus sp. During Exposure to Elevated Levels of Cu and Zn and After Withdrawal of Metal Stress | Protoplasma229(1): 1-9 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Biochemical | LOEL | 2 | days | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., and J.P. Gaur | Physiological Behavior of Scenedesmus sp. During Exposure to Elevated Levels of Cu and Zn and After Withdrawal of Metal Stress | Protoplasma229(1): 1-9 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Population | LOEL | 7 | days | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Accumulation | LOEL | 7 | days | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Population | LOEL | 2 | days | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., and J.P. Gaur | Physiological Behavior of Scenedesmus sp. During Exposure to Elevated Levels of Cu and Zn and After Withdrawal of Metal Stress | Protoplasma229(1): 1-9 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Population | LOEL | 6 | hours | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Biochemical | LOEL | 6 | hours | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2016/03/25 | ||||||
| 藻類 | Navicula sp. | Population | NOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Guasch,H., E. Navarro, A. Serra, and S. Sabater | Phosphate Limitation Influences the Sensitivity to Copper in Periphytic Algae | Freshw. Biol.49(4): 463-473 | 2004 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Cellular Effects | NOEL | 2 | days | 25 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., and J.P. Gaur | Physiological Behavior of Scenedesmus sp. During Exposure to Elevated Levels of Cu and Zn and After Withdrawal of Metal Stress | Protoplasma229(1): 1-9 | 2006 | 2016/03/25 | ||||||
| 藻類 | Navicula sp. | Population | NOEL | 12 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Guasch,H., E. Navarro, A. Serra, and S. Sabater | Phosphate Limitation Influences the Sensitivity to Copper in Periphytic Algae | Freshw. Biol.49(4): 463-473 | 2004 | 2016/03/25 | ||||||
| 藻類 | Chlorella sp. | Physiology | 1 | hours | 6000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Filippis,L.F. | The Effect of Heavy Metal Compounds on the Permeability of Chlorella Cells | Z. Pflanzenphysiol.92(1): 39-49 | 1979 | 2016/03/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC10 | 3 | days | 47.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2016/03/25 | ||||||
| 藻類 | Scenedesmus sp. | Biochemical | LOEL | 2 | days | 2.5 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tripathi,B.N., and J.P. Gaur | Physiological Behavior of Scenedesmus sp. During Exposure to Elevated Levels of Cu and Zn and After Withdrawal of Metal Stress | Protoplasma229(1): 1-9 | 2006 | 2016/03/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 179.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 103 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 285.1 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 316.7 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus acutus var. acutus | cell number | EC50 | 144 | hours | 0.48 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 154.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus acutus var. acutus | cell number | EC50 | 24 | hours | 2.59 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 96 | hours | 200 | μg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 34.6 | μg/mL | 0 ug/ml / >0-<=100 ug/ml | 16 ECOTOX | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2022/01/25 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 36.5 | μg/mL | 0 ug/ml / >0-<=100 ug/ml | 16 ECOTOX | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2022/01/25 | |||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 24 | hours | 45 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 24 | hours | 21.5 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Chlorella protothecoides | growth rate | LC50 | days | 31.77 | mg/L | 0 mg/L / 0.063-64.51 mg/L | 16 ECOTOX | Aliotta,G., G. Pinto, and A. Pollio | Observations on Tolerance to Heavy Metals of Four Green Algae in Relation to pH | G. Bot. Ital. 117(5/6): 247-251 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 121.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Chlorella pyrenoidosa | cell number | EC50 | 96 | hours | 1.01 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 65.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 26.9 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Chlorella pyrenoidosa | cell number | EC50 | 168 | hours | 0.56 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Chlorella pyrenoidosa | cell number | EC50 | 48 | hours | 1.24 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Chlorella pyrenoidosa | cell number | EC50 | 120 | hours | 0.87 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Chlorella pyrenoidosa | cell number | EC50 | 72 | hours | 1.14 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Scenedesmus acutus var. acutus | cell number | EC50 | 96 | hours | 0.73 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Chlorella pyrenoidosa | cell number | EC50 | 144 | hours | 0.71 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 51 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 198.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus acutus var. acutus | cell number | EC50 | 72 | hours | 14.31 | μM | 0 uM / 1 uM / 2 uM / 3 uM / 4 uM / 5 uM / 7.5 uM / 10 uM / 12 uM / 15 uM / 18 uM / 20 uM | 16 ECOTOX | Wen,Y., H. Chen, C. Shen, M. Zhao, and W. Liu | Enantioselectivity Tuning of Chiral Herbicide Dichlorprop by Copper: Roles of Reactive Oxygen Species | Environ. Sci. Technol.45(11): 4778-4784 | 2011 | 2022/01/25 | |||||
| 藻類 | Chlorella saccharophila | cell number | EC50 | 96 | hours | 550 | μg/L | 16 ECOTOX | Rachlin,J.W., T.E. Jensen, B. Warkentine, and H.H. Lehman | The Growth Response of the Green Alga (Chlorella saccharophila) to Selected Concentrations of the Heavy Metals Cd, Cu, Pb, and Zn | In: D.D.Hemphill (Ed.), Trace Substances in Environmental Health, University of Missouri, Columbia, MO:145-154 | 1982 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 105 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 90 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Navicula incerta | growth | EC50 | 96 | hours | 10450 | μg/L | 16 ECOTOX | Rachlin,J.W., T.E. Jensen, and B. Warkentine | The Growth Response of the Diatom Navicula incerta to Selected Concentrations of the Metals: Cadmium, Copper, Lead and Zinc | Bull. Torrey Bot. Club110(2): 217-223 | 1983 | 2022/01/25 | ||||||
| 藻類 | Chlorella pyrenoidosa | cell number | EC50 | 24 | hours | 1.45 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Chlorella saccharophila | growth rate | LC50 | days | 1.98 | mg/L | 0 mg/L / 0.063-64.51 mg/L | 16 ECOTOX | Aliotta,G., G. Pinto, and A. Pollio | Observations on Tolerance to Heavy Metals of Four Green Algae in Relation to pH | G. Bot. Ital. 117(5/6): 247-251 | 1983 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 72 | hours | 7.5 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Chlorella saccharophila | growth rate | LC50 | days | 15.88 | mg/L | 0 mg/L / 0.063-64.51 mg/L | 16 ECOTOX | Aliotta,G., G. Pinto, and A. Pollio | Observations on Tolerance to Heavy Metals of Four Green Algae in Relation to pH | G. Bot. Ital. 117(5/6): 247-251 | 1983 | 2022/01/25 | ||||||
| 藻類 | Chlorella protothecoides | growth rate | LC50 | days | 1.98 | mg/L | 0 mg/L / 0.063-64.51 mg/L | 16 ECOTOX | Aliotta,G., G. Pinto, and A. Pollio | Observations on Tolerance to Heavy Metals of Four Green Algae in Relation to pH | G. Bot. Ital. 117(5/6): 247-251 | 1983 | 2022/01/25 | ||||||
| 藻類 | Chlorella saccharophila | Mortality | LC50 | 42 | days | 0.0000158 | mol | 16 ECOTOX | Pinto,G., and R. Taddei | Evaluation of Toxic Effects of Heavy Metals on Unicellular Algae. V - Analysis of the Inhibition Manifesting Itself with an Increased Lag Phase | Boll. Soc. Nat. Napoli95:303-316 | 1986 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 127.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus acutus var. acutus | cell number | EC50 | 120 | hours | 0.55 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 19 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 24 | hours | 23 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 24 | hours | 30 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Dunaliella tertiolecta | growth | EC50 | 72 | hours | 38800 | μg/L | 16 ECOTOX | Edding,M., and F. Tala | Copper Transfer and Influence on a Marine Food Chain | Bull. Environ. Contam. Toxicol.57(4): 617-624 | 1996 | 2022/01/25 | ||||||
| 藻類 | Anabaena doliolum | Mortality | LD50 | 15 | days | 8 | μmol/L | 16 ECOTOX | Rai,L.C., B. Tyagi, P.K. Rai, and N. Mallick | Interactive Effects of UV-B and Heavy Metals (Cu and Pb) on Nitrogen and Phosphorus Metabolism of a N2-Fixing Cyanobacterium Anabaena doliolum | Environ. Exp. Bot.39(3): 221-231 | 1998 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 16.5 | μg/mL | 0 ug/ml / 5 ug/ml / 10 ug/ml / 15 ug/ml / 20 ug/ml / 25 ug/ml / 30 ug/ml / 35 ug/ml / 40 ug/ml / 45 ug/ml / 50 ug/ml | 16 ECOTOX | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2022/01/25 | |||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 72 | hours | 5.6 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 48 | hours | 9.8 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 72 | hours | 3.45 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 506.8 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 44 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 171.9 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 16 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 66.1 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | IC50 | 72 | hours | 280 | μg/L | 16 ECOTOX | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 55 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | IC50 | 72 | hours | 150 | μg/L | 16 ECOTOX | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus acutus var. acutus | cell number | EC50 | 48 | hours | 0.41 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | cell number | IC50 | 72 | hours | 147 | μg/L | 16 ECOTOX | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 453.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 127.7 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth rate | EC50 | 96 | hours | 274.022 | μg/L | 0 ug/L / 250 ug/L / 500 ug/L / 750 ug/L / 1000 ug/L / 1500 ug/L / 2000 ug/L | 16 ECOTOX | Atay,S., and H.B. Ozkoc | Effect of Sediment on the Bioavailability and Toxicity of Copper and Zinc to a Green Alga | Fresenius Environ. Bull.19(12a): 3018-3027 | 2010 | 2022/01/25 | |||||
| 藻類 | Phaeodactylum tricornutum | growth rate | EC50 | 96 | hours | 279.241 | μg/L | 0 mg/L / 0.25 mg/L / 0.50 mg/L / 0.75 mg/L / 1.00 mg/L / 1.50 mg/L / 2.00 mg/L | 16 ECOTOX | Atay,S., H.B. Ozkoc, and V.R. Uslu | Sediment Toxicity for Evaluation of Sediment Quality Guidelines and Bioavailability of Copper and Zinc | Fresenius Environ. Bull.22(4): 1031-1042 | 2013 | 2022/01/25 | |||||
| 藻類 | Phaeodactylum tricornutum | growth rate | EC50 | 96 | hours | 0.231 | mg/L | 16 ECOTOX | Cid,A., P. Fidalgo, C. Herrero, and J. Abalde | Toxic Action of Copper on the Membrane System of a Marine Diatom Measured by Flow Cytometry | Cytometry25(1): 32-36 | 1996 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 96 | hours | 4.83 | mg/L | 0 mg/L / 2.5 mg/L / 5.0 mg/L / 7.5 mg/L / 10.0 mg/L / 12.5 mg/L / 15.0 mg/L / 17.5 mg/L | 16 ECOTOX | Lam,P.K.S., P.F. Wut, A.C.W. Chan, and R.S.S. Wu | Individual and Combined Effects of Cadmium and Copper on the Growth Response of Chlorella vulgaris | Environ. Toxicol.14(3): 347-353 | 1999 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 234 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 37.3 | μg/mL | 0 ug/ml / >0-<=100 ug/ml | 16 ECOTOX | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2022/01/25 | |||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 72 | hours | 7 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 39.9 | μg/mL | 0 ug/ml / >0-<=100 ug/ml | 16 ECOTOX | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2022/01/25 | |||||
| 藻類 | Navicula seminulum var. hustedtii | growth rate | EC50 | 96 | hours | 795 | μg/L | 16 ECOTOX | Academy of Natural Sciences | The Sensitivity of Aquatic Life to Certain Chemicals Commonly Found in Industrial Wastes | Final Rep.No.RG-3965(C2R1), U.S.Public Health Service Grant, Acad.of Nat.Sci., Philadelphia, PA:89 p. | 1960 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 35 | μg/mL | 0 ug/ml / >0-<=100 ug/ml | 16 ECOTOX | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 138.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 178.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 72 | hours | 12 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 48 | hours | 6.75 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Phaeodactylum tricornutum | growth rate | EC50 | 96 | hours | 409.12 | μg/L | 0 mg/L / 0.25 mg/L / 0.50 mg/L / 0.75 mg/L / 1.00 mg/L / 1.50 mg/L / 2.00 mg/L | 16 ECOTOX | Atay,S., H.B. Ozkoc, and V.R. Uslu | Sediment Toxicity for Evaluation of Sediment Quality Guidelines and Bioavailability of Copper and Zinc | Fresenius Environ. Bull.22(4): 1031-1042 | 2013 | 2022/01/25 | |||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 48 | hours | 30 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 9 | days | 0.8 | mg/dm3 | 16 ECOTOX | Latala,A., and W. Surosz | Growth of Four Planktonic Algae from Brackish Water in the Presence of Heavy Metals | Pol. Arch. Hydrobiol.46(2): 131-154 | 1999 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 48 | hours | 24 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 24 | hours | 22.5 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Phaeodactylum tricornutum | growth rate | EC50 | 48 | hours | 0.208 | mg/L | 16 ECOTOX | Cid,A., P. Fidalgo, C. Herrero, and J. Abalde | Toxic Action of Copper on the Membrane System of a Marine Diatom Measured by Flow Cytometry | Cytometry25(1): 32-36 | 1996 | 2022/01/25 | ||||||
| 藻類 | Dunaliella tertiolecta | growth | EC50 | 48 | hours | 44760 | μg/L | 16 ECOTOX | Edding,M., and F. Tala | Copper Transfer and Influence on a Marine Food Chain | Bull. Environ. Contam. Toxicol.57(4): 617-624 | 1996 | 2022/01/25 | ||||||
| 藻類 | Phaeodactylum tricornutum | growth rate | EC50 | 24 | hours | 0.667 | mg/L | 16 ECOTOX | Cid,A., E. Torres, C. Herrero, and J.E. Abalde | Disorders Provoked by Copper in the Marine Diatom Phaeodactylum tricornutum in Short-Time Exposure Assays | Cah.Biol.Mar.38(3): 201-206 | 1997 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | Chlorophyll | IC50 | 7 | days | 14 | μmol/dm3 | 16 ECOTOX | Kral'ova,K., K. Kissova, and O. Svajlenova | Effects of Carboxylatocopper(II) Complexes on Photosynthesizing Organisms | Chem. Inz. Ekol.7(10): 1076-1083 | 2000 | 2022/01/25 | ||||||
| 藻類 | Skeletonema costatum | growth | IC50 | 96 | hours | 45 | μg/L | 16 ECOTOX | Nassiri,Y., J.L. Mansot, J. Wery, T. Ginsburger-Vogel, and J.C. Amiard | Ultrastructural and Electron Energy Loss Spectroscopy Studies of Sequestration Mechanisms of Cd and Cu in the Marine Diatom Skeletonema costatum | Arch. Environ. Contam. Toxicol.33(2): 147-155 | 1997 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus quadricauda | growth rate | IC50 | 72 | hours | 0.18 | mg/L | 16 ECOTOX | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | IC50 | 7 | days | 19.2 | μmol/dm3 | 16 ECOTOX | Kral'ova,K., K. Kissova, and O. Svajlenova | Effects of Carboxylatocopper(II) Complexes on Photosynthesizing Organisms | Chem. Inz. Ekol.7(10): 1076-1083 | 2000 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | cell number | LC50 | 15 | minutes | 2 | mg/L | 16 ECOTOX | Rai,P.K., and L.C. Rai | Interactive Effects of UV-B and Cu on Photosynthesis, Uptake and Metabolism of Nutrients in a Green Alga Chlorella vulgaris Under Simulated Ozone Column | J. Gen. Appl. Microbiol.43(5): 281-288 | 1997 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 60.7 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 37 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth rate | EC50 | 96 | hours | 381.153 | μg/L | 0 ug/L / 250 ug/L / 500 ug/L / 750 ug/L / 1000 ug/L / 1500 ug/L / 2000 ug/L | 16 ECOTOX | Atay,S., and H.B. Ozkoc | Effect of Sediment on the Bioavailability and Toxicity of Copper and Zinc to a Green Alga | Fresenius Environ. Bull.19(12a): 3018-3027 | 2010 | 2022/01/25 | |||||
| 藻類 | Scenedesmus acutus var. acutus | Biomass | EC50 | 96 | hours | 50 | μg/L | 16 ECOTOX | Yan,H., and G. Pan | Toxicity and Bioaccumulation of Copper in Three Green Microalgal Species | Chemosphere49(5): 471-476 | 2002 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus acutus var. acutus | cell number | EC50 | 168 | hours | 0.49 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 168.1 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 37 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Long-Term Acclimation of Pseudokirchneriella subcapitata (Korshikov) Hindak to Different Copper Concentrations: Changes in Tolerance and Physiology | Aquat. Toxicol.68(1): 61-74 | 2004 | 2022/01/25 | ||||||
| 藻類 | Dunaliella tertiolecta | growth | EC50 | 24 | hours | 58930 | μg/L | 16 ECOTOX | Edding,M., and F. Tala | Copper Transfer and Influence on a Marine Food Chain | Bull. Environ. Contam. Toxicol.57(4): 617-624 | 1996 | 2022/01/25 | ||||||
| 藻類 | Navicula seminulum var. hustedtii | growth rate | EC50 | 96 | hours | 815 | μg/L | 16 ECOTOX | Academy of Natural Sciences | The Sensitivity of Aquatic Life to Certain Chemicals Commonly Found in Industrial Wastes | Final Rep.No.RG-3965(C2R1), U.S.Public Health Service Grant, Acad.of Nat.Sci., Philadelphia, PA:89 p. | 1960 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 356 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 105 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | IC50 | 4 | days | 72.3 | μg/L | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | IC50 | 72 | hours | 64.2 | μg/L | 16 ECOTOX | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 25 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 130.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus acutus var. acutus | cell number | EC50 | 72 | hours | 0.66 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 56 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 160 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 341 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 29.1 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Thalassiosira pseudonana | growth | EC50 | 48 | hours | 8.2 | μg/L | 16 ECOTOX | Erickson,S.J. | Toxicity of Copper to Thalassiosira pseudonana in Unenriched Inshore Seawater | J. Phycol.8(4): 318-323 | 1972 | 2022/01/25 | ||||||
| 藻類 | Chlorella pyrenoidosa | Biomass | EC50 | 96 | hours | 68 | μg/L | 16 ECOTOX | Yan,H., and G. Pan | Toxicity and Bioaccumulation of Copper in Three Green Microalgal Species | Chemosphere49(5): 471-476 | 2002 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 7.8 | μg/mL | 0 ug/ml / 5 ug/ml / 10 ug/ml / 15 ug/ml / 20 ug/ml / 25 ug/ml / 30 ug/ml / 35 ug/ml / 40 ug/ml / 45 ug/ml / 50 ug/ml | 16 ECOTOX | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 104.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 156.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth rate | EC50 | 96 | hours | 400 | μg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 12 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 88.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | Growth | EC50 | 3 | days | 7000 | μg/L | 16 ECOTOX | Wren,M.J., and D. McCarroll | A Simple and Sensitive Bioassay for the Detection of Toxic Materials Using a Unicellular Green Alga | Environ. Pollut.64(1): 87-91 | 1990 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 134.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 38.6 | μg/mL | 0 ug/ml / >0-<=100 ug/ml | 16 ECOTOX | Kursten,D., J. Cao, A. Funfak, P. Muller, and J.M. Kohler | Cultivation of Chlorella vulgaris in Microfluid Segments and Microtoxicological Determination of Their Sensitivity Against CuCl2 in the Nanoliter Range | Eng. Life Sci.11(6): 580-587 | 2011 | 2022/01/25 | |||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 113 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 142.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 145 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth | EC50 | 5 | days | 215 | μg/L | 16 ECOTOX | Allen,H.E., C. Blatchley, and T.D. Brisbin | An Algal Assay Method for Determination of Copper Complexation Capacities of Natural Waters | Bull. Environ. Contam. Toxicol.30(4): 448-455 | 1983 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 490.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 311.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC50 | 72 | hours | 30.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 296 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 2021/10/25 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 333 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 446 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) 225-235 | 2021/10/25 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 987 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | 2021/10/25 | ||||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 111 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 380 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 200 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) 225-235 | 2021/10/25 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 99 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 254 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) 225-235 | 2021/10/25 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 506 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 2021/10/25 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 602 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 773 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 440 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | 2021/10/25 | ||||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 208 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 364 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 238 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 60 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) 225-235 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 368 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 152 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 84 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 36.9 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 33.9 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 52.7 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 245 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 51 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 268 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 174 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 55 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 105 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 99 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 151 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 122 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 685 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 161 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 30 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 108 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 59 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 209 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 346 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 37 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 16.5 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 756 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 193 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 102 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 190 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 163 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 156 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 32 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 194 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 281 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 178 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 205 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 93 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 35 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 97.4 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 100 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 219 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 113 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 65.4 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 462 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 199 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 18 | μg/L [meas. (initial) element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 811 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 824 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 230 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 92 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 35 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 46 | μg/L [meas. (initial) element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 84 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 97.4 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 194 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 33.9 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 32 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 65.4 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 152 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 113 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 16.5 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 163 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Selenastrum capricornutum | biomass | EC50 | 72 | hours | 35 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Nyholm | 2022/02/08 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 245 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Selenastrum capricornutum | growth inhibition | EC50 | 72 | hours | 47 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Nyholm | 2022/02/08 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 52.7 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 36.9 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Scenedesmus subspicata | growth inhibition | EC50 | 72 | hours | 120 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Schäfer H, Hettler H, Fritsche U, Pitzen G, Roderer G, & Wenzel A | Biotests using unicellular algae and ciliates for predicting long-term effects of toxicants. Long-term effects of toxicants | Ecotoxicol Environ Saf, 27 | 2022/02/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | EC50 | 72 | hours | 108 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Navicula tripunctata | cell number | NOEL | 6 | days | 15 | μg/L | 16 ECOTOX | Guasch,H., E. Navarro, A. Serra, and S. Sabater | Phosphate Limitation Influences the Sensitivity to Copper in Periphytic Algae | Freshw. Biol.49(4): 463-473 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEL | 6 | days | 10 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 藻類 | Navicula cryptocephala | cell number | NOEL | 6 | days | 15 | μg/L | 16 ECOTOX | Guasch,H., E. Navarro, A. Serra, and S. Sabater | Phosphate Limitation Influences the Sensitivity to Copper in Periphytic Algae | Freshw. Biol.49(4): 463-473 | 2004 | 2022/01/25 | ||||||
| 藻類 | Navicula sp. | cell number | NOEL | 12 | days | 15 | μg/L | 16 ECOTOX | Guasch,H., E. Navarro, A. Serra, and S. Sabater | Phosphate Limitation Influences the Sensitivity to Copper in Periphytic Algae | Freshw. Biol.49(4): 463-473 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 67.7 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Biomass | NOEC | weeks | 35 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Long-Term Acclimation of Pseudokirchneriella subcapitata (Korshikov) Hindak to Different Copper Concentrations: Changes in Tolerance and Physiology | Aquat. Toxicol.68(1): 61-74 | 2004 | 2022/01/25 | |||||||
| 藻類 | Chlorella vulgaris | Photosynthesis | LOEL | 2 | hours | 2 | mg/L | 16 ECOTOX | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2022/01/25 | ||||||
| 藻類 | Navicula cryptocephala | cell number | NOEL | 12 | days | 15 | μg/L | 16 ECOTOX | Guasch,H., E. Navarro, A. Serra, and S. Sabater | Phosphate Limitation Influences the Sensitivity to Copper in Periphytic Algae | Freshw. Biol.49(4): 463-473 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth rate | NOEC | 4 | days | 262 | nM | 16 ECOTOX | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEL | 4 | days | 160 | μg/L | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 藻類 | Navicula sp. | cell number | NOEL | 6 | days | 15 | μg/L | 16 ECOTOX | Guasch,H., E. Navarro, A. Serra, and S. Sabater | Phosphate Limitation Influences the Sensitivity to Copper in Periphytic Algae | Freshw. Biol.49(4): 463-473 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth rate | NOEL | 72 | hours | 33.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2022/01/25 | ||||||
| 藻類 | Navicula tripunctata | cell number | NOEL | 12 | days | 15 | μg/L | 16 ECOTOX | Guasch,H., E. Navarro, A. Serra, and S. Sabater | Phosphate Limitation Influences the Sensitivity to Copper in Periphytic Algae | Freshw. Biol.49(4): 463-473 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEL | 6 | days | 15 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 9 | days | 0.094 | mg/dm3 | 16 ECOTOX | Latala,A., and W. Surosz | Growth of Four Planktonic Algae from Brackish Water in the Presence of Heavy Metals | Pol. Arch. Hydrobiol.46(2): 131-154 | 1999 | 2022/01/25 | ||||||
| 藻類 | Phaeodactylum tricornutum | Chlorophyll A concentration | LOEL | 12 | hours | 0.5 | mg/L | 16 ECOTOX | Cid,A., E. Torres, C. Herrero, and J.E. Abalde | Disorders Provoked by Copper in the Marine Diatom Phaeodactylum tricornutum in Short-Time Exposure Assays | Cah.Biol.Mar.38(3): 201-206 | 1997 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | Photosynthesis | LOEL | 2 | hours | 2 | mg/L | 16 ECOTOX | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus quadricauda | Biomass | LOEC | days | 2.5 | μg/L | 16 ECOTOX | Comeaux,J.L. | Effects of Copper on Benthic Communities in Artificial Microcosms | Ph.D.Thesis, Virginia Polytechnic Institute and State University, Blacksburg, VA:172 p. | 1996 | 2022/01/25 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | LOEC | 9 | days | 0.1 | mg/dm3 | 16 ECOTOX | Latala,A., and W. Surosz | Growth of Four Planktonic Algae from Brackish Water in the Presence of Heavy Metals | Pol. Arch. Hydrobiol.46(2): 131-154 | 1999 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | Chlorophyll A concentration | LOEL | 15 | days | 2 | mg/L | 16 ECOTOX | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2022/01/25 | ||||||
| 藻類 | Dunaliella tertiolecta | growth | NOEC | 72 | hours | 12500 | μg/L | 16 ECOTOX | Edding,M., and F. Tala | Copper Transfer and Influence on a Marine Food Chain | Bull. Environ. Contam. Toxicol.57(4): 617-624 | 1996 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 5 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 118.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | NOEC | 9 | days | 0.1 | mg/dm3 | 16 ECOTOX | Latala,A., and W. Surosz | Growth of Four Planktonic Algae from Brackish Water in the Presence of Heavy Metals | Pol. Arch. Hydrobiol.46(2): 131-154 | 1999 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | NOEC | 4 | days | 262 | nM | 16 ECOTOX | Knauert,S., and K. Knauer | The Role of Reactive Oxygen Species in Copper Toxicity to Two Freshwater Green Algae | J. Phycol.44(2): 311-319 | 2008 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | Chlorophyll A concentration | LOEL | 15 | days | 2 | mg/L | 16 ECOTOX | Rai,P.K., N. Mallick, and L.C. Rai | Effect of Cu and Ni on Growth, Mineral Uptake, Photosynthesis and Enzyme Activities of Chlorella vulgaris at Different pH Values | Biomed. Environ. Sci.7(1): 56-67 | 1994 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 55.1 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 134.7 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 42.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 14.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 55.8 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 175.9 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 94 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 25 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 61.8 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 52 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 43.9 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 53.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 56.9 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 46.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 53.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 47.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 148.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 25.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 63.9 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Phaeodactylum tricornutum | Chlorophyll A concentration | NOEL | 12 | hours | 0.25 | mg/L | 16 ECOTOX | Cid,A., E. Torres, C. Herrero, and J.E. Abalde | Disorders Provoked by Copper in the Marine Diatom Phaeodactylum tricornutum in Short-Time Exposure Assays | Cah.Biol.Mar.38(3): 201-206 | 1997 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 92.7 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 42.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 16.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 89.7 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 68.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 18.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 146.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 15.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 91.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 96.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 93.7 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 33.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 75.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 66.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Navicula seminulum | Biomass | NOEC | days | 2.5 | μg/L | 16 ECOTOX | Comeaux,J.L. | Effects of Copper on Benthic Communities in Artificial Microcosms | Ph.D.Thesis, Virginia Polytechnic Institute and State University, Blacksburg, VA:172 p. | 1996 | 2022/01/25 | |||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 91.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 19.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 53.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 49.4 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 49.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 57.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 59.9 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 40.8 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus sp. | Photosynthesis | LOEL | 7 | days | 2.5 | μM | 16 ECOTOX | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth rate | NOEC | 4 | days | 100 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 89.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 97.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 111.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 112.8 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 54.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 174 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 59.1 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 110.9 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | IC10 | 4 | days | 5.7 | μg/L | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Biomass | LOEC | 24 | hours | 10 | μg/L | 16 ECOTOX | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Biomass | LOEC | weeks | 60 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Long-Term Acclimation of Pseudokirchneriella subcapitata (Korshikov) Hindak to Different Copper Concentrations: Changes in Tolerance and Physiology | Aquat. Toxicol.68(1): 61-74 | 2004 | 2022/01/25 | |||||||
| 藻類 | Scenedesmus acutus var. acutus | cell number | LOEC | hours | 0.36 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | ||||||
| 藻類 | Navicula seminulum | Biomass | LOEC | days | 5 | μg/L | 16 ECOTOX | Comeaux,J.L. | Effects of Copper on Benthic Communities in Artificial Microcosms | Ph.D.Thesis, Virginia Polytechnic Institute and State University, Blacksburg, VA:172 p. | 1996 | 2022/01/25 | |||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 170.8 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Biomass | LOEC | 96 | hours | 10 | μg/L | 16 ECOTOX | Thompson,J.A. | Cellular Fluorescence Capacity as an Endpoint in Algal Toxicity Testing | Chemosphere35(9): 2027-2037 | 1997 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | growth rate | LOEL | 72 | hours | >40～60 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 60.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 37.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus sp. | Photosynthesis | LOEL | 6 | hours | 2.5 | μM | 16 ECOTOX | Tripathi,B.N., S.K. Mehta, A. Amar, and J.P. Gaur | Oxidative Stress in Scenedesmus sp. During Short- and Long-Term Exposure to Cu2+ and Zn2+ | Chemosphere62(4): 538-544 | 2006 | 2022/01/25 | ||||||
| 藻類 | Anabaena doliolum | growth rate | LOEL | 15 | days | 1 | μM | 16 ECOTOX | Tripathi,B.N., S.K. Mehta, and J.P. Gaur | Differential Sensitivity of Anabaena doliolum to Cu and Zn in Batch and Semicontinuous Cultures | Ecotoxicol. Environ. Saf.56(2): 311-318 | 2003 | 2022/01/25 | ||||||
| 藻類 | Anabaena doliolum | growth rate | LOEL | 15 | days | 1 | μM | 16 ECOTOX | Tripathi,B.N., S.K. Mehta, and J.P. Gaur | Differential Sensitivity of Anabaena doliolum to Cu and Zn in Batch and Semicontinuous Cultures | Ecotoxicol. Environ. Saf.56(2): 311-318 | 2003 | 2022/01/25 | ||||||
| 藻類 | Scenedesmus sp. | cell number | LOEL | 48 | hours | 2.5 | μM | 16 ECOTOX | Tripathi,B.N., and J.P. Gaur | Physiological Behavior of Scenedesmus sp. During Exposure to Elevated Levels of Cu and Zn and After Withdrawal of Metal Stress | Protoplasma229(1): 1-9 | 2006 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | EC10 | 72 | hours | 43.3 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | Chlorella pyrenoidosa | cell number | LOEC | hours | 0.36 | mg/L | 0 mg/L / 0.36 mg/L / 0.57 mg/L / 0.90 mg/L / 1.43 mg/L | 16 ECOTOX | Pan,X., C. Wan, M. Li, X. Chen, Y. Zou, and J. Chang | Monitoring of Copper Contamination: A Laboratory Study About the Possibility to Use Chlorophyll Fluorescence Parameters of Three Green Microalgae | Fresenius Environ. Bull.22(3a): 800-807 | 2013 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | cell number | NOEC | 72 | hours | 53.7 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, and C.R. Janssen | Development and Field Validation of a Predictive Copper Toxicity Model for the Green Alga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.22(10): 2454-2465 | 2003 | 2022/01/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 52.9 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 164 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 61.8 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.A.C. & Janssen, C.R. | A biotic ligand model predicting acute copper toxicity to Daphnia magna: the effects of calcium, magnesium, sodium, potassium and pH | Environ.Sci.Technol. 36, 48-84 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 56.4 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Kramer, K.J.M. et al. | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environ Toxicol Chem. 2004; 23(12):2971-80. | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 23.1 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Adam N, Vakurov A, Knapen D, Blust R | The chronic toxicity of CuO nanoparticles and copper salt to Daphnia magna | Journal of Hazardous materials 283:416-422 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 170.8 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 67.7 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Alsop D, Wood CM | Metal uptake and acute toxicity in zebrafish: common mechanisms across multiple metals | Aquatic Toxicology 105:385-393 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 53.7 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Alsop D, Wood CM | Metal uptake and acute toxicity in zebrafish: common mechanisms across multiple metals | Aquatic Toxicology 105:385-393 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 54.6 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 53.3 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 35.4 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 15.7 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 17.9 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 35.4 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 91.3 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Skeletonema costatum | growth rate | NOEC | 72 | hours | 7.54 | μg/L [meas. (geom. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 17.9 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 19.3 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 49 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Simpson, S. et al. | Effect of declining toxicant concentrations on algal bioassay endpoints | ; Environmental Toxicology and Chemistry, 22(9): 2073-2079 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 23.1 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 37.6 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 56.4 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 94.7 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 23.1 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 13.5 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 65.5 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 52.9 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 60.2 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 59.1 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 65.5 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.A.C et al. | Refinement and field validation of a biotic ligand model predicting acute copper toxicity to Daphnia magna | Comparative biochemistry and physiology part C, 133, 243-258 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 15.7 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 19.3 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Little EE, Calfee RD, Linder G | Toxicity of copper to early-life stage Kootenai river white sturgeon, Columbia river white sturgeon, and rainbow trout | Archives of Environmental Toxicology and Chemistry 63:400-408 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 61.8 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 49 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Little EE, Calfee RD, Linder G | Toxicity of copper to early-life stage Kootenai river white sturgeon, Columbia river white sturgeon, and rainbow trout | Archives of Environmental Toxicology and Chemistry 63:400-408 | 2021/10/25 | |||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 97.2 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 112.8 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 49.4 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 19.4 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 174 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Alsop D, Wood CM | Metal uptake and acute toxicity in zebrafish: common mechanisms across multiple metals | Aquatic Toxicology 105:385-393 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 40.8 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 89.2 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 164 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 94.7 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Phaeodactylum tricornutum | growth rate | NOEC | 72 | hours | 5.7 | μg/L [meas. (geom. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 111.2 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Phaeodactylum tricornutum | growth rate | EC10 | 72 | hours | 2.9 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 49 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 57.5 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 110.6 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 164 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 65.5 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 61.8 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 52.9 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | cell number | NOEC | 72 | hours | 63.9 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 藻類 | Scenedesmus subspicata | growth inhibition | NOEC | 72 | hours | 5.6 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Schäfer H, Hettler H, Fritsche U, Pitzen G, Roderer G, & Wenzel A | Biotests using unicellular algae and ciliates for predicting long-term effects of toxicants. Long-term effects of toxicants | Ecotoxicol Environ Saf, 27 | 2022/02/08 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 56.4 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 17.9 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 19.3 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 23.1 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 35.4 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 94.7 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 15.7 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Nitocra spinipes | Mortality | LOEC | 6 | days | 440 | μg/L | 0 ug/L / 24 ug/L / 49 ug/L / 110 ug/L / 220 ug/L / 440 ug/L | 16 ECOTOX | Ytreberg,E., J. Karlsson, and B. Eklund | Comparison of Toxicity and Release Rates of Cu and Zn from Anti-Fouling Paints Leached in Natural and Artificial Brackish Seawater | Sci. Total Environ.408(12): 2459-2466 | 2010 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Survival | NOEC | 8 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Growth (Length) | NOEC | 40 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Palaemonetes pugio | Development/Stage | LOEL | days | 9 | μg/L | 16 ECOTOX | Manyin,T., and C.L. Rowe | Reproductive and Life Stage-Specific Effects of Aqueous Copper on the Grass Shrimp, Palaemonetes pugio | Mar. Environ. Res.69(3): 152-157 | 2009 | 2022/01/25 | |||||||
| 甲殻類 | Daphnia magna | Survival | NOEL | 6 | days | 15 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 40 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 96 | hours | 352 | μg/L | 6.5 ug/L / 50.1-57.5 ug/L / 97.0-114 ug/L / 197-206 ug/L / 322-329 ug/L / 726-743 ug/L / 1730 ug/L | 16 ECOTOX | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Filtration rate | NOEL | 6 | days | 10 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Nitocra spinipes | Mortality | NOEC | 6 | days | 220 | μg/L | 0 ug/L / 24 ug/L / 49 ug/L / 110 ug/L / 220 ug/L / 440 ug/L | 16 ECOTOX | Ytreberg,E., J. Karlsson, and B. Eklund | Comparison of Toxicity and Release Rates of Cu and Zn from Anti-Fouling Paints Leached in Natural and Artificial Brackish Seawater | Sci. Total Environ.408(12): 2459-2466 | 2010 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Filtration rate | NOEL | 6 | days | 10 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Filtration rate | NOEL | 6 | days | 15 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Palaemonetes pugio | Survival | NOEL | 240 | days | 26 | μg/L | 16 ECOTOX | Manyin,T., and C.L. Rowe | Reproductive and Life Stage-Specific Effects of Aqueous Copper on the Grass Shrimp, Palaemonetes pugio | Mar. Environ. Res.69(3): 152-157 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Filtration rate | NOEL | 6 | days | 15 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Filtration rate | NOEL | 6 | days | 10 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Survival | NOEL | 6 | days | 10 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Survival | NOEC | 14 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Palaemonetes pugio | Development/Stage | NOEL | days | 26 | μg/L | 16 ECOTOX | Manyin,T., and C.L. Rowe | Reproductive and Life Stage-Specific Effects of Aqueous Copper on the Grass Shrimp, Palaemonetes pugio | Mar. Environ. Res.69(3): 152-157 | 2009 | 2022/01/25 | |||||||
| 甲殻類 | Nitocra spinipes | Normal development | NOEC | 6 | days | 49 | μg/L | 0 ug/L / 24 ug/L / 49 ug/L / 110 ug/L / 220 ug/L / 440 ug/L | 16 ECOTOX | Ytreberg,E., J. Karlsson, and B. Eklund | Comparison of Toxicity and Release Rates of Cu and Zn from Anti-Fouling Paints Leached in Natural and Artificial Brackish Seawater | Sci. Total Environ.408(12): 2459-2466 | 2010 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 96 | hours | 25 | μg/L | 16 ECOTOX | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 14 | days | 38 | μg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Growth (Length) | LOEC | 40 | days | 150 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Nitocra spinipes | Normal development | LOEC | 6 | days | 110 | μg/L | 0 ug/L / 24 ug/L / 49 ug/L / 110 ug/L / 220 ug/L / 440 ug/L | 16 ECOTOX | Ytreberg,E., J. Karlsson, and B. Eklund | Comparison of Toxicity and Release Rates of Cu and Zn from Anti-Fouling Paints Leached in Natural and Artificial Brackish Seawater | Sci. Total Environ.408(12): 2459-2466 | 2010 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Survival | LOEL | days | 120 | μg/L | 16 ECOTOX | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2022/01/25 | |||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 96 | hours | 78.9 | μg/L | 16.8 ug/L / 59-59.4 ug/L / 122-128 ug/L / 258 ug/L / 481 ug/L / 1010 ug/L / 1850 ug/L | 16 ECOTOX | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Filtration rate | LOEL | 6 | days | 15 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Palaemonetes pugio | Survival | NOEL | 240 | days | 26 | μg/L | 16 ECOTOX | Manyin,T., and C.L. Rowe | Reproductive and Life Stage-Specific Effects of Aqueous Copper on the Grass Shrimp, Palaemonetes pugio | Mar. Environ. Res.69(3): 152-157 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Palaemonetes pugio | Survival | NOEL | 240 | days | 26 | μg/L | 16 ECOTOX | Manyin,T., and C.L. Rowe | Reproductive and Life Stage-Specific Effects of Aqueous Copper on the Grass Shrimp, Palaemonetes pugio | Mar. Environ. Res.69(3): 152-157 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Filtration rate | LOEL | 6 | days | 10 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Survival | NOEC | 4 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 14 | days | 130 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 96 | hours | 9.28 | μg/L | 2.3 ug/L / 7.98-10.2 ug/L / 10.8-14.3 ug/L / 30.6 ug/L / 58.4 ug/L / 138 ug/L / 291 ug/L | 16 ECOTOX | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 14 | days | 96 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 96 | hours | 50 | μg/L | 16 ECOTOX | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Mortality | LC50 | 96 | hours | 10.4 | μg/L | 16 ECOTOX | Lytle,R.D. | In Situ Copper Toxicity Tests: Applying Likelihood Ratio Tests to Daphnia pulex Incubations in Keweenaw Peninsula Waters | J. Great Lakes Res.25(4): 744-759 | 1999 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Survival | NOEL | days | 90 | μg/L | 16 ECOTOX | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2022/01/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 96 | hours | 130 | μg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 14 | days | 75 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Palaemonetes pugio | Mortality | NR-ZERO | 21 | days | 26 | μg/L | 16 ECOTOX | Manyin,T., and C.L. Rowe | Reproductive and Life Stage-Specific Effects of Aqueous Copper on the Grass Shrimp, Palaemonetes pugio | Mar. Environ. Res.69(3): 152-157 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | LC50 | 9 | days | 894 | μg/L | 16 ECOTOX | Weber,R.E., A. De Zwaan, and A. Bang | Interactive Effects of Ambient Copper and Anoxic, Temperature and Salinity Stress on Survival and Hemolymph and Muscle Tissue Osmotic Effectors in Mytilus edulis | J. Exp. Mar. Biol. Ecol.159(2): 135-156 | 1992 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Developmental changes | EC50 | 72 | hours | >21～35 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Growth | EC50 | 10 | days | 6 | μg/L | 16 ECOTOX | Redpath,K.J. | Growth Inhibition and Recovery in Mussels (Mytilus edulis) Exposed to Low Copper Concentrations | J. Mar. Biol. Assoc. U.K.65(2): 421-431 | 1985 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | NR-LETH | 21 | days | 100 | μg/L | 0 ug/L / 10 ug/L / 100 ug/L / 500 ug/L | 16 ECOTOX | Brooks,S.J., E. Farmen, L.S. Heier, E. Blanco-Rayon, and U. Izagirre | Differences in Copper Bioaccumulation and Biological Responses in Three Mytilus Species | Aquat. Toxicol.160:1-12 | 2015 | 2022/01/25 | |||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 6.8 | days | 310 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | LC95 | 96 | hours | 0.21 | mg/L | 16 ECOTOX | Nelson,D.A., J.E. Miller, and A. Calabrese | Effect of Heavy Metals on Bay Scallops, Surf Clams, and Blue Mussels in Acute and Long-Term Exposures | Arch. Environ. Contam. Toxicol.17(5): 595-600 | 1988 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 7 | days | 30 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | LC50 | 15 | days | 400 | μg/L | 16 ECOTOX | Beaumont,A.R., G. Tserpes, and M.D. Budd | Some Effects of Copper on the Veliger Larvae of the Mussel Mytilus edulis and the Scallop Pecten maximus (Mollusca, Bivalvia) | Mar. Environ. Res.21(4): 299-309 | 1987 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | days | 230 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | |||||||
| 甲殻類 | Mytilus edulis | Mortality | LC50 | 96 | hours | 122 | μg/L | 16 ECOTOX | Nelson,D.A., J.E. Miller, and A. Calabrese | Effect of Heavy Metals on Bay Scallops, Surf Clams, and Blue Mussels in Acute and Long-Term Exposures | Arch. Environ. Contam. Toxicol.17(5): 595-600 | 1988 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | LC05 | 96 | hours | 0.07 | mg/L | 16 ECOTOX | Nelson,D.A., J.E. Miller, and A. Calabrese | Effect of Heavy Metals on Bay Scallops, Surf Clams, and Blue Mussels in Acute and Long-Term Exposures | Arch. Environ. Contam. Toxicol.17(5): 595-600 | 1988 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | LC50 | 14 | days | 146 | μg/L | 16 ECOTOX | Weber,R.E., A. De Zwaan, and A. Bang | Interactive Effects of Ambient Copper and Anoxic, Temperature and Salinity Stress on Survival and Hemolymph and Muscle Tissue Osmotic Effectors in Mytilus edulis | J. Exp. Mar. Biol. Ecol.159(2): 135-156 | 1992 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 6.8 | days | 180 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Valve closure | LOEL | hours | 0.8 | μM | 16 ECOTOX | Curtis,T.M., R. Williamson, and M.H. Depledge | Simultaneous, Long-Term Monitoring of Valve and Cardiac Activity in the Blue Mussel Mytilus edulis Exposed to Copper | Mar. Biol.136(5): 837-846 | 2000 | 2022/01/25 | |||||||
| 甲殻類 | Mytilus edulis | Mortality | LT50 | 12.5 | days | 400 | μg/L | 16 ECOTOX | Hoare,K., and J. Davenport | Size-Related Variation in the Sensitivity of the Mussel, Mytilus edulis, to Copper | J. Mar. Biol. Assoc. U.K.74(4): 971-973 | 1994 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | LT50 | 9 | days | 400 | μg/L | 16 ECOTOX | Hoare,K., and J. Davenport | Size-Related Variation in the Sensitivity of the Mussel, Mytilus edulis, to Copper | J. Mar. Biol. Assoc. U.K.74(4): 971-973 | 1994 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | LT50 | 5.3 | days | 400 | μg/L | 16 ECOTOX | Hoare,K., and J. Davenport | Size-Related Variation in the Sensitivity of the Mussel, Mytilus edulis, to Copper | J. Mar. Biol. Assoc. U.K.74(4): 971-973 | 1994 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | LT50 | 6.5 | days | 400 | μg/L | 16 ECOTOX | Hoare,K., and J. Davenport | Size-Related Variation in the Sensitivity of the Mussel, Mytilus edulis, to Copper | J. Mar. Biol. Assoc. U.K.74(4): 971-973 | 1994 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Mortality | LT50 | 6.8 | days | 400 | μg/L | 16 ECOTOX | Hoare,K., and J. Davenport | Size-Related Variation in the Sensitivity of the Mussel, Mytilus edulis, to Copper | J. Mar. Biol. Assoc. U.K.74(4): 971-973 | 1994 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Valve closure | NOEL | hours | 0.08 | μM | 16 ECOTOX | Curtis,T.M., R. Williamson, and M.H. Depledge | Simultaneous, Long-Term Monitoring of Valve and Cardiac Activity in the Blue Mussel Mytilus edulis Exposed to Copper | Mar. Biol.136(5): 837-846 | 2000 | 2022/01/25 | |||||||
| 甲殻類 | Mytilus edulis | Mortality | NR-LETH | 6 | days | 100 | μg/L | 16 ECOTOX | Martin,J.L.M. | Schema of Lethal Action of Copper on Mussels | Bull. Environ. Contam. Toxicol.21(6): 808-814 | 1979 | 2022/01/25 | ||||||
| 甲殻類 | Mercenaria mercenaria | Mortality | LC50 | days | 16.4 | μg/L | 16 ECOTOX | Calabrese,A., J.R. MacInnes, D.A. Nelson, and J.E. Miller | Survival and Growth of Bivalve Larvae Under Heavy-Metal Stress | Mar. Biol.41:179-184 | 1977 | 2022/01/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | NOEL | 15 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/23 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Behavior | NOEC | 1 | hours | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Juchelka,C.M., and T.W. Snell | Rapid Toxicity Assessment Using Ingestion Rate of Cladocerans and Ciliates | Arch. Environ. Contam. Toxicol.28(4): 508-512 | 1995 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LOEL | 15 | days | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/23 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | LOEL | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 40 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEL | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | LOEC | 40 | days | 150 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | LOEC | 4 | days | 10 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEL | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 11.172 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 14 | days | >130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 14 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 14 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 10 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Accumulation | LOEC | 7 | days | 80 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 10 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 100 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 40 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 11.172 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | <10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 3.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | LOEC | 21 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 398 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 320 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 7.92 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 102.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 148 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 61.18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cairns,M.A., A.V. Nebeker, J.H. Gakstatter, and W.L. Griffis | Toxicity of Copper-Spiked Sediments to Freshwater Invertebrates | Environ. Toxicol. Chem.3(3): 435-445 | 1984 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 398 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 369 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 17.47 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 16.93 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 257 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 466 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 347 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 426 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 21.55 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 42.68 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 14.49 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 12.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 77 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cairns,M.A., A.V. Nebeker, J.H. Gakstatter, and W.L. Griffis | Toxicity of Copper-Spiked Sediments to Freshwater Invertebrates | Environ. Toxicol. Chem.3(3): 435-445 | 1984 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 5.38 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 2.64 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 131 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 59.77 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 50.46 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 100.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 1.505 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 2.092 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 77.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 36.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 2.387 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 10.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 279 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 2.21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 14 | days | 38 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 16.16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 79.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 10.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 38 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 9.14 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 14 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 31.77 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 16.35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 11.99 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 69 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsui,M.T.K., W.X. Wang, and L.M. Chu | Influence of Glyphosate and Its Formulation (Roundup) on the Toxicity and Bioavailability of Metals to Ceriodaphnia dubia | Environ. Pollut.138(1): 59-68 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 335 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 421 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 354 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 400 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 7.88 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 12.94 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 57.28 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsui,M.T.K., W.X. Wang, and L.M. Chu | Influence of Glyphosate and Its Formulation (Roundup) on the Toxicity and Bioavailability of Metals to Ceriodaphnia dubia | Environ. Pollut.138(1): 59-68 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 26 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 20.97 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 5.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 1.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 1.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 38.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 51.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 14 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 10.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 3.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 0.9133 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 4.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 107 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 179 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 40 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 107 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 6.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Population | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | 1 | days | 0.47761 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kolupayev,Y.I. | Sensitivity of Test Functions as a Basis for Selecting Bioassays for Aquatic Toxicity | Hydrobiol. J.25(5): 52-54 | 1990 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Biochemical | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Accumulation | 12～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | ||||||||||
| 甲殻類 | Daphnia magna | Accumulation | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | |||||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 7 | days | 78 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mahar,A.M., and M.C. Watzin | Effects of Metal and Organophosphate Mixtures on Ceriodaphnia dubia Survival and Reproduction | Environ. Toxicol. Chem.24(7): 1579-1586 | 2005 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | 7 | days | 78 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mahar,A.M., and M.C. Watzin | Effects of Metal and Organophosphate Mixtures on Ceriodaphnia dubia Survival and Reproduction | Environ. Toxicol. Chem.24(7): 1579-1586 | 2005 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Population | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Mortality | 2 | days | 130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pittinger,C.A., D.J. Versteeg, B.A. Blatz, and E.M. Meiers | Environmental Toxicology of Succinate Tartrates | Aquat. Toxicol.24(1-2): 83-102 | 1992 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Mortality | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Biochemical | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Reproduction | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Mortality | 1000～25000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bodar,C.W.M., A.V.D. Zee, P.A. Voogt, H. Wynne, and D.I. Zandee | Toxicity of Heavy Metals to Early Life Stages of Daphnia magna | Ecotoxicol. Environ. Saf.17(3): 333-338 | 1989 | 2016/03/25 | ||||||||||
| 甲殻類 | Daphnia magna | Growth | 21 | days | 12.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Buchner, and H. Van Dijk | Intermittent Flow System for Population Toxicity Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol.40(4): 496-502 | 1988 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Growth | 21 | days | 36.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Buchner, and H. Van Dijk | Intermittent Flow System for Population Toxicity Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol.40(4): 496-502 | 1988 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | 21 | days | 9.5～29 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Behavior | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 31.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 2 | days | 13 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 2 | days | 186 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2016/03/25 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 1.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 81 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Reproduction | 10～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2016/03/25 | ||||||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Biochemical | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Growth | 10～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gerasimov,Y.L. | Toxic Action of Copper on Daphnia magna (Crustacea, Cladocera) at Different Feed Concentrations | Dokl. Akad. Nauk SSSR293(6): 1510-1513 | 1987 | 2016/03/25 | ||||||||||
| 甲殻類 | Daphnia magna | Growth | 40 | days | 1～150 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Mortality | 10～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gerasimov,Y.L. | Toxic Action of Copper on Daphnia magna (Crustacea, Cladocera) at Different Feed Concentrations | Dokl. Akad. Nauk SSSR293(6): 1510-1513 | 1987 | 2016/03/25 | ||||||||||
| 甲殻類 | Daphnia magna | Biochemical | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Population | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Physiology | 40 | days | 1～100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Accumulation | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | |||||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 10 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 14 | days | >130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 14 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | NOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 12 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 92.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 14 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 96.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 14 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | <10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 40 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Accumulation | NOEC | 7 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 2.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEL | 21 | days | 183 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEL | 21 | days | 130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | NOEL | 7 | days | >0～<15.9 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 123 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 2 | days | 0.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 116 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 196 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 81.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Cellular Effects | NOEL | 15 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 1 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Behavior | NOEC | 1 | hours | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Juchelka,C.M., and T.W. Snell | Rapid Toxicity Assessment Using Ingestion Rate of Cladocerans and Ciliates | Arch. Environ. Contam. Toxicol.28(4): 508-512 | 1995 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2.67 | days | 27 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,B.G. | The Apparent Thresholds of Toxicity to Daphnia magna for Chlorides of Various Metals when Added to Lake Erie Water | Trans. Am. Fish. Soc.78:96-113 | 1948 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Behavior | NOEL | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Growth | NOEL | 15 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NOEL | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEL | 15 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Population | NOEL | 15 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NOEL | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Accumulation | NOEL | 7 | days | 163.4 | その他others [ug/g dry fd] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 97 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 245 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 14 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 290 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 70.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 251 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 104 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 14 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 315 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 1.892 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 372 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 24.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 15.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 275 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 20 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Population | EC50 | 21 | days | 16.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Buchner, and H. Van Dijk | Intermittent Flow System for Population Toxicity Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol.40(4): 496-502 | 1988 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 79.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 26.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 71 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 260 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | <10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 70.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 354 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 354 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 113 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 41 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Elnabarawy,M.T., A.N. Welter, and R.R. Robideau | Relative Sensitivity of Three Daphnid Species to Selected Organic and Inorganic Chemicals | Environ. Toxicol. Chem.5(4): 393-398 | 1986 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 322 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | <295 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 48 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 7 | days | 70.5 | その他others [ug/g dry fd] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 25.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 7 | days | 7.5 | その他others [ng/d] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | No Group Code | EC50 | 2 | days | 14.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | No Group Code | EC50 | 4 | days | 9.28 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | No Group Code | EC50 | 2 | days | 102 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | No Group Code | EC50 | 4 | days | 78.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 128 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | No Group Code | EC50 | 4 | days | 352 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 236 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 607 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 9.22 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 542 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 97.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 129 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 53.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 257 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | No Group Code | EC50 | 2 | days | 634 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 192 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 64 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 81.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 55.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 332 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 1090 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 638 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 31.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 311 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 5.62 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 261 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 212 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 86.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >30～<35 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 14 | days | 86 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 304 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 65.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 74.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 354 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 45.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 17 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 81.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 7.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 75.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 281 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 204 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 51.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 72.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 71.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 50.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 57.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 56.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 70.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 58.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 61 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 51.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 38.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 45.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 46.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 68.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 56.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 69 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 68.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 308 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 53.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 72.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 99 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 6.35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 50.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 9.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 93 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 67.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 310 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 74.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 56.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 198 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 76.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 55.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 320 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 87 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 21.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >150～<200 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 69 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >250～<300 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 292 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 124 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 34 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 60.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 109 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 151 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 210 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 70.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >320 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 193 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 430 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 296 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 68.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 90.44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 102.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 39.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 110.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 78.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 29.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 44.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 2.221 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 5.02 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 37 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 3.087 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 2.139 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 17.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 49.59 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 3.274 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC25 | 7 | days | 2.5 | その他others [ng/d] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 4 | days | 130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 65 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC25 | 7 | days | 14.4 | その他others [ug/g dry fd] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 5.3 | その他others [ng/d] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 45.3 | その他others [ug/g dry fd] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 45.3 | その他others [ug/g dry fd] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 5.3 | その他others [ng/d] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC100 | 2 | days | 11.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsui,M.T.K., W.X. Wang, and L.M. Chu | Influence of Glyphosate and Its Formulation (Roundup) on the Toxicity and Bioavailability of Metals to Ceriodaphnia dubia | Environ. Pollut.138(1): 59-68 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 71.34 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 7 | days | 70.5 | その他others [ug/g dry fd] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 95.55 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 4 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 7 | days | 7.5 | その他others [ng/d] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 4 | days | 16.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hunt,J.W., B.S. Anderson, B.M. Phillips, P.N. Nicely, R.S. Tjeerdema, H.M. Puckett, M. Stephenson, K. Worcester, and V. | Ambient Toxicity due to Chlorpyrifos and Diazinon in a Central California Coastal Watershed | Environ. Monit. Assess.82:83-112 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 26.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 23.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 4 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 2 | days | 0.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 2.2501 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Growth | LOEL | 15 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LOEL | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Cellular Effects | LOEL | 15 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEL | 15 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Population | LOEL | 15 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEC | 40 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Behavior | LOEL | 7 | days | 74.7 | その他others [ug/g dry fd] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 2 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | LOEL | 7 | days | 15.9 | その他others [ug/g dry fd] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | 12 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | |||||||||
| 甲殻類 | Daphnia magna | Accumulation | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2016/03/25 | |||||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 207 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LOEL | 7 | days | 74.7 | その他others [ug/g dry fd] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 14 | days | 96 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 20.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 78.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 58.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 29.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 357 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 322 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 14 | days | >130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 14.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 21 | days | 69 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Buchner, and H. Van Dijk | Intermittent Flow System for Population Toxicity Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol.40(4): 496-502 | 1988 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 302 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 932 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 60.92 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 9.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 7.89 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 824 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 126 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 129 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 139 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 116 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 109 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 200 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 87.8 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 275 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 142 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 222 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 245 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 162 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 221 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 230 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 201 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 0.8478 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 108 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 56.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 70.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 22.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 5.49 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 7.97 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 106 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 107 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 172 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 5.57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 106 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 671 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 113 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 159 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 221 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 15.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 241 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 10.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 139 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 173 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 91.9 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 138 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 102 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 47 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 149 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 97.1 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 81.6 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 174 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 198 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 1 | days | 22 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sorvari,J., and M. Sillanpaa | Influence of Metal Complex Formation on Heavy Metal and Free EDTA and DTPA Acute Toxicity Determined by Daphnia magna | Chemosphere33(6): 1119-1127 | 1996 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 76.5 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 221 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 57.6 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 175 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 251 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 343 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 243 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 340 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 333 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 240 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 197 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 225 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 223 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 204 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 191 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 247 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 221 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 21 | days | 44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | LOEC | 8 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Reproduction | LOEC | 14 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | LOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | LOEC | 2 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | LOEC | 8 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | LOEC | 8 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Reproduction | LOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 11.172 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 40 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 14 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | LOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., S.P. Glaholt, Z. Smith, G. Smagghe, C.R. Janssen, J.K. Colbourne, J.R. Shaw, and K.A.C. De Schamphelaere | Functional Characterization of Four Metallothionein Genes in Daphnia pulex Exposed to Environmental Stressors | Aquat. Toxicol.110/111:54-65 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 40 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 100 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | LOEC | 40 | days | 150 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 10 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Accumulation | LOEC | 7 | days | 80 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | LOEC | 21 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 14 | days | >130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEL | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEL | 15 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 2 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Accumulation | NOEC | 7 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 12 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Behavior | LOEL | 7 | days | 74.7 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 96.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 20.97 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 13.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | LOEC | 2 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 11.172 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 1 | days | 45 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 10 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | LOEL | 7 | days | 15.9 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LOEL | 7 | days | 74.7 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 2 | days | 0.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEL | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Growth | LOEL | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Cellular Effects | LOEL | 15 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | LOEL | 15 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Population | LOEL | 15 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | LOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cairns,M.A., A.V. Nebeker, J.H. Gakstatter, and W.L. Griffis | Toxicity of Copper-Spiked Sediments to Freshwater Invertebrates | Environ. Toxicol. Chem.3(3): 435-445 | 1984 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | LC50 | 2 | days | 24 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | LC50 | 4 | days | 10.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lytle,R.D. | In Situ Copper Toxicity Tests: Applying Likelihood Ratio Tests to Daphnia pulex Incubations in Keweenaw Peninsula Waters | J. Great Lakes Res.25(4): 744-759 | 1999 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 65 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 149 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 1.892 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 12.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 69 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 1.505 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 21.55 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 102.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 398 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 398 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 426 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 14.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 44.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 131 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 3.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 421 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsui,M.T.K., W.X. Wang, and L.M. Chu | Influence of Glyphosate and Its Formulation (Roundup) on the Toxicity and Bioavailability of Metals to Ceriodaphnia dubia | Environ. Pollut.138(1): 59-68 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 7 | days | 70.5 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 16.16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 38 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 4 | days | 16.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hunt,J.W., B.S. Anderson, B.M. Phillips, P.N. Nicely, R.S. Tjeerdema, H.M. Puckett, M. Stephenson, K. Worcester, and V. | Ambient Toxicity due to Chlorpyrifos and Diazinon in a Central California Coastal Watershed | Environ. Monit. Assess.82:83-112 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 400 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 335 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 56.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 302 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 10.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 71.34 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 77.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 357 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 59.77 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 37.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 7.88 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 5.02 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 10.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 3.274 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 29.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 58.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 2.21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 257 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 6.68 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 2.221 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 23.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 100.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 76.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 5.38 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 14.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 49.59 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 14 | days | >130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 20.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 2.387 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 50.46 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 57.28 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 466 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 14 | days | >130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 78.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 29.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 37 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 61.18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 0.9133 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 3.087 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 14 | days | 96 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 347 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 39.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | LC50 | 2 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 17.47 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 7.89 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 369 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 26 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 24.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 279 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 7 | days | 7.5 | その他others [ng/d] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 78.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 376 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 11.99 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 322 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 4 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 79.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 2.64 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 9.56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 36.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 9.14 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 207 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Behavior | NOEL | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 8 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Accumulation | NOEL | 7 | days | 163.4 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Cellular Effects | NOEL | 15 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEL | 15 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Growth | NOEL | 1 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hunter,K., and G. Pyle | Morphological Responses of Daphnia pulex to Chaoborus americanus Kairomone in the Presence and Absence of Metals | Environ. Toxicol. Chem.23(5): 1311-1316 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Population | NOEL | 15 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NOEL | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | NOEL | 7 | days | >0～<15.9 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 116 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 40 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 2 | days | 0.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEL | 21 | days | 130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | <10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 107 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Reproduction | NOEL | 1 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hunter,K., and G. Pyle | Morphological Responses of Daphnia pulex to Chaoborus americanus Kairomone in the Presence and Absence of Metals | Environ. Toxicol. Chem.23(5): 1311-1316 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Behavior | NOEL | 6 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NOEL | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEL | 15 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEL | 21 | days | 183 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 81 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 51.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 24～48 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2017/03/15 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 1.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 14 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 1 | days | 135 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 31.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 1.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 38.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 179 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., S.P. Glaholt, Z. Smith, G. Smagghe, C.R. Janssen, J.K. Colbourne, J.R. Shaw, and K.A.C. De Schamphelaere | Functional Characterization of Four Metallothionein Genes in Daphnia pulex Exposed to Environmental Stressors | Aquat. Toxicol.110/111:54-65 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 5.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 4.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 81.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 196 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 3.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 6.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 107 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 2.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 123 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 125 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 10 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | <10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2.67 | days | 27 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,B.G. | The Apparent Thresholds of Toxicity to Daphnia magna for Chlorides of Various Metals when Added to Lake Erie Water | Trans. Am. Fish. Soc.78:96-113 | 1948 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 40 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 320 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 77 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cairns,M.A., A.V. Nebeker, J.H. Gakstatter, and W.L. Griffis | Toxicity of Copper-Spiked Sediments to Freshwater Invertebrates | Environ. Toxicol. Chem.3(3): 435-445 | 1984 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 14 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Reproduction | NOEC | 21 | days | 0.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 1 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | 2 | days | 1.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 2 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | NOEC | 4 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | NOEC | 10 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Reproduction | NOEC | 12 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | NOEC | 2 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | NOEC | 12 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 1 | days | 270 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 1 | days | 270 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 1 | days | 270 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 1 | days | 270 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., S.P. Glaholt, Z. Smith, G. Smagghe, C.R. Janssen, J.K. Colbourne, J.R. Shaw, and K.A.C. De Schamphelaere | Functional Characterization of Four Metallothionein Genes in Daphnia pulex Exposed to Environmental Stressors | Aquat. Toxicol.110/111:54-65 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., S.P. Glaholt, Z. Smith, G. Smagghe, C.R. Janssen, J.K. Colbourne, J.R. Shaw, and K.A.C. De Schamphelaere | Functional Characterization of Four Metallothionein Genes in Daphnia pulex Exposed to Environmental Stressors | Aquat. Toxicol.110/111:54-65 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 2 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 354 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 14 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | NOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 14 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 1 | days | 270 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 2 | days | 186 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 1 | days | 270 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 2 | days | 13 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Growth | NOEC | 2 | days | 56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | NOEC | 8 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 4 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | NOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 4 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 16 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | NOEC | 14 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 4 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEC | 2 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 1 | days | 270 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 12.94 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 46.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 9.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 149 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 221 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 172 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 57.6 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 7 | days | 70.5 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 204 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 372 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 71.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsui,M.T.K., W.X. Wang, and L.M. Chu | Influence of Glyphosate and Its Formulation (Roundup) on the Toxicity and Bioavailability of Metals to Ceriodaphnia dubia | Environ. Pollut.138(1): 59-68 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 332 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 48 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 81.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | <10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 14 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 50.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 72.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | NOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | NOEC | 21 | days | 156.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | NOEC | 21 | days | 156.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | NOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | NOEC | 21 | days | 156.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 68.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 14 | days | 86 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 50.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 56.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 53.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 38.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 51.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 58.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 45.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 61 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 70.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 68.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 45.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 69 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 51.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 56.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 75.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 21 | days | 57.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 15.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 354 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 320 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 70.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 91.9 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 230 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 139 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 7.97 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Reproduction | EC50 | 21 | days | 5.11 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., S.P. Glaholt, Z. Smith, G. Smagghe, C.R. Janssen, J.K. Colbourne, J.R. Shaw, and K.A.C. De Schamphelaere | Functional Characterization of Four Metallothionein Genes in Daphnia pulex Exposed to Environmental Stressors | Aquat. Toxicol.110/111:54-65 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 192 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >320 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 212 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 15.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | EC50 | 2 | days | 102 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | EC50 | 4 | days | 78.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 60.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 245 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 129 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 221 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 671 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 71 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 311 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 356 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | NOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 354 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 542 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 415 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 126 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 159 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 97.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 56.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 70.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 99 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 14 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 70.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 139 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 191 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 204 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 222 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 251 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 193 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 932 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LOEC | 21 | days | 156.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 58.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 20.04 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 59 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 25.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 21.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 40.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 26.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 23.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia hyalina | Mortality | LC50 | 2 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Baudouin,M.F., and P. Scoppa | Acute Toxicity of Various Metals to Freshwater Zooplankton | Bull. Environ. Contam. Toxicol.12(6): 745-751 | 1974 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 358.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 23.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 318.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 95.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 80.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Behavior | LOEC | 1 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LOEC | 21 | days | 229.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Growth | LOEC | 21 | days | 156.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | LOEC | 21 | days | 229.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | LOEC | 21 | days | 156.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | LOEC | 21 | days | 156.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Growth | NOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 38.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | EC50 | 21 | days | 85 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Growth | EC50 | 21 | days | 356 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | EC50 | 21 | days | 216 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Physiology | EC50 | 1 | days | 0.0809 | その他others [µmol/L] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Choueri,R.B., P.K. Gusso-Choueri, M.G. Gama Melao, A.T. Lombardi, and A.A. Henriques Vieira | The Influence of Cyanobacterium Exudates on Copper Uptake and Toxicity to a Tropical Freshwater Cladoceran | J. Plankton Res.31(10): 1225-1233 | 2009 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | EC50 | 21 | days | 88 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Growth | EC50 | 21 | days | 102 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | EC50 | 21 | days | 80 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | EC50 | 21 | days | 98 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | EC50 | 21 | days | 269 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Growth | EC50 | 21 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | EC50 | 21 | days | 227 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | EC50 | 21 | days | 79 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | LOEC | 21 | days | 21.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia reticulata | Physiology | EC50 | 2 | days | 23 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Elnabarawy,M.T., A.N. Welter, and R.R. Robideau | Relative Sensitivity of Three Daphnid Species to Selected Organic and Inorganic Chemicals | Environ. Toxicol. Chem.5(4): 393-398 | 1986 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | EC50 | 21 | days | 87 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Growth | EC50 | 21 | days | 160 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | EC50 | 21 | days | 72 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | EC50 | 21 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 38 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 58.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 25.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 48.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LC50 | 2 | days | 75.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | EC50 | 21 | days | 80 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Physiology | NOEC | 1 | days | 9.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | LOEC | 21 | days | 229.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Reproduction | NOEC | 33 | days | 4.83 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Mortality | NOEC | 33 | days | 4.83 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Reproduction | NOEC | 33 | days | 4.83 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Reproduction | NOEC | 33 | days | 4.83 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Reproduction | NOEC | 33 | days | 4.83 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | NOEC | 21 | days | 9.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Behavior | NOEC | 1 | days | 21.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Behavior | NOEC | 1 | days | 21.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Growth | NOEC | 33 | days | 4.83 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Physiology | NOEC | 1 | days | 21.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Behavior | LOEC | 1 | days | 5.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | NOEC | 21 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | NOEC | 21 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | NOEC | 21 | days | 5.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | NOEC | 21 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | NOEC | 21 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | NOEC | 21 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | NOEC | 21 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | NOEC | 21 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | NOEC | 21 | days | 21.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 113 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Physiology | NOEC | 1 | days | 9.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | LOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Growth | LOEC | 21 | days | 5.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | LOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | LOEC | 21 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Behavior | LOEC | 1 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Behavior | LOEC | 1 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Physiology | LOEC | 1 | days | 21.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Physiology | LOEC | 1 | days | 42.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Physiology | LOEC | 1 | days | 21.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | LOEC | 21 | days | 5.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Reproduction | NOEC | 33 | days | 4.83 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Behavior | NOEC | 1 | days | 21.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Growth | LOEC | 21 | days | 5.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | LOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | LOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Reproduction | LOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Mortality | LOEC | 21 | days | 85.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Growth | LOEC | 21 | days | 5.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Accumulation | LOEC | 1 | days | 0.01 | その他others [µmol/L] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Choueri,R.B., P.K. Gusso-Choueri, M.G. Gama Melao, A.T. Lombardi, and A.A. Henriques Vieira | The Influence of Cyanobacterium Exudates on Copper Uptake and Toxicity to a Tropical Freshwater Cladoceran | J. Plankton Res.31(10): 1225-1233 | 2009 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Population | LOEC | 33 | days | 3.2 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Growth | LOEC | 21 | days | 3.2 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia sp. Ceriodaphnia cornuta | Reproduction | LOEC | 2.61 | days | 3.2 | その他others [µg/d/org] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia longispina | Population | LOEC | 21 | days | 9.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 21 | days | 69 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Buchner, and H. Van Dijk | Intermittent Flow System for Population Toxicity Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol.40(4): 496-502 | 1988 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 354 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 9.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 34 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 281 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 93 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 148 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 110.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 16.93 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 7.92 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 26.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 16.35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 240 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 2.092 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 102.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 56.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 267 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 90.44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | LC50 | 2 | days | 17.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | LC50 | 2 | days | 22 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 10.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Mortality | LC50 | 21 | days | 0.003～3 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 4 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 20 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 31.77 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 260 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 261 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 70.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 53.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 225 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 5.57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 241 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 76.5 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 116 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 106 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 221 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 1090 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 292 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 72.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >250～<300 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 87 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 315 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 17 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 200 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 322 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 310 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 223 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | EC50 | 2 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Elnabarawy,M.T., A.N. Welter, and R.R. Robideau | Relative Sensitivity of Three Daphnid Species to Selected Organic and Inorganic Chemicals | Environ. Toxicol. Chem.5(4): 393-398 | 1986 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 5.3 | その他others [ng/d] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 47 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 87.8 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 198 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 221 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 21 | days | 44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | EC50 | 2 | days | 634 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 236 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 275 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 21.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 6.35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 14 | days | 38 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 5.3 | その他others [ng/d] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 104 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 45.3 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC100 | 2 | days | 11.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsui,M.T.K., W.X. Wang, and L.M. Chu | Influence of Glyphosate and Its Formulation (Roundup) on the Toxicity and Bioavailability of Metals to Ceriodaphnia dubia | Environ. Pollut.138(1): 59-68 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 42.68 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 14.49 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 0.8478 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 2 | days | 2.139 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 95.55 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 60.92 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 4 | days | 130 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Physiology | LC50 | 2 | days | 78.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 1 | days | 2.2501 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 45.3 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 824 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 75 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | LOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEC | 40 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 14 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Accumulation | LOEC | 40 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | LOEC | 4 | days | 10 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | LOEC | 14 | days | 90 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 4.212 | その他others [ng] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 92.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 290 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | Cellular Effects | NOEC | 4 | days | 6.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 175 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 64 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 607 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 257 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 5.49 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 9.22 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 97 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 304 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 207 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 308 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 162 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 109 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 81.6 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 201 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 5.62 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 247 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 340 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 251 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 343 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 26.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 173 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 638 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 301 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 67.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 245 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 124 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 74.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | EC50 | 4 | days | 352 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >30～<35 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 74.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 55.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | EC50 | 2 | days | 14.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | EC50 | 4 | days | 9.28 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | <295 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 41 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Elnabarawy,M.T., A.N. Welter, and R.R. Robideau | Relative Sensitivity of Three Daphnid Species to Selected Organic and Inorganic Chemicals | Environ. Toxicol. Chem.5(4): 393-398 | 1986 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 97.1 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 138 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 197 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 67.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Population | EC50 | 21 | days | 16.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Buchner, and H. Van Dijk | Intermittent Flow System for Population Toxicity Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol.40(4): 496-502 | 1988 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 129 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 25.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 31.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 81.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 68.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 210 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 65.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 78.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 151 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 211 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 174 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 128 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 430 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 7.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 243 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 1 | days | 22 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sorvari,J., and M. Sillanpaa | Influence of Metal Complex Formation on Heavy Metal and Free EDTA and DTPA Acute Toxicity Determined by Daphnia magna | Chemosphere33(6): 1119-1127 | 1996 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 104 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 314 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 55.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >150～<200 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 7 | days | 7.5 | その他others [ng/d] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 86.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 69 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 56.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 76.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 107 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 106 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 102 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 142 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Physiology | EC50 | 2 | days | 22.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 109 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 275 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 333 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 108 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 198 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 296 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 79.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2017/03/15 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 10.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 113 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2017/03/15 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2017/03/15 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 67.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 301 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 78.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 104 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | >200～<250 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 314 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 207 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 356 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 211 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 9.56 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 65 | μg/L | 16 ECOTOX | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 322 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 71.34 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 10.4 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 78.5 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 2.387 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 59.77 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 200 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 302 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 10.5 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 3.274 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 3.087 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 24 | hours | 426 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 21.55 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 149 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 279 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 2.092 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 12.94 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 16.35 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 50.46 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Mortality | LC50 | 48 | hours | 24 | μg/L | 16 ECOTOX | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 49.59 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～100 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 354 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 9.14 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 2.221 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 335 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 24 | hours | 466 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 56.6 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 79.2 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 23.1 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 30 | μg/L | 16 ECOTOX | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 148 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 69 | μg/L | 16 ECOTOX | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 5.02 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Mortality | LC50 | 48 | hours | 22 | μg/L | 16 ECOTOX | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 24 | hours | 357 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 14.5 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 14.49 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 30 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 80.7 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 6.68 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～100 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia reticulata | Immobilization | EC50 | 48 | hours | 23 | μg/L | 16 ECOTOX | Elnabarawy,M.T., A.N. Welter, and R.R. Robideau | Relative Sensitivity of Three Daphnid Species to Selected Organic and Inorganic Chemicals | Environ. Toxicol. Chem.5(4): 393-398 | 1986 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia cornuta | Immobilization | EC50 | 24 | hours | 0.0000000809 | mol/L | 0 mol/L / 0.00000001 mol/L / 0.00000004 mol/L / 0.00000007 mol/L / 0.0000001 mol/L / 0.000001 mol/L | 16 ECOTOX | Choueri,R.B., P.K. Gusso-Choueri, M.G. Gama Melao, A.T. Lombardi, and A.A. Henriques Vieira | The Influence of Cyanobacterium Exudates on Copper Uptake and Toxicity to a Tropical Freshwater Cladoceran | J. Plankton Res.31(10): 1225-1233 | 2009 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 25.8 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 23.2 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 358.4 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 23.7 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 59 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia hyalina | Mortality | LC50 | 48 | hours | 5 | μg/L | 16 ECOTOX | Baudouin,M.F., and P. Scoppa | Acute Toxicity of Various Metals to Freshwater Zooplankton | Bull. Environ. Contam. Toxicol.12(6): 745-751 | 1974 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 40.4 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 20.04 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 48.5 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >0～41.8 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 38.3 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Holmesimysis costata | Mortality | LC50 | 96 | hours | 16 | μg/L | 16 ECOTOX | Asato,S.L., and D.J. Reish | The Effects of Heavy Metals on the Survival and Feeding of Holmesimysis costata (Crustacea: Mysidacea) | In: Proceedings of the 7th International Symposium on Marine Biology, California State University, Long Beach, CA:113-120 | 1988 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 318.6 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 25.2 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 75.1 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Holmesimysis costata | Mortality | LC50 | 96 | hours | 27.2 | μg/L | 16 ECOTOX | Hunt,J.W., B.S. Anderson, S.L. Turpen, A.R. Coulon, M. Martin, F.H. Palmer, and J.J. Janik | Marine Bioassay Project. 4th Report. Experimental Evaluation of Effluent Toxicity Testing Protocols with Giant Kelp, Mysids, Red Abalone, and Topsmelt | No.89-5WQ, State Water Resources Control Board, State of California, Sacramento, CA:144- | 1989 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 58.1 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 38 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 26.1 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 21.9 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 58.4 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 95.1 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Holmesimysis costata | Survival | NOEC | 96 | hours | 11 | μg/L | 16 ECOTOX | Hunt,J.W., B.S. Anderson, S.L. Turpen, A.R. Coulon, M. Martin, F.H. Palmer, and J.J. Janik | Marine Bioassay Project. 4th Report. Experimental Evaluation of Effluent Toxicity Testing Protocols with Giant Kelp, Mysids, Red Abalone, and Topsmelt | No.89-5WQ, State Water Resources Control Board, State of California, Sacramento, CA:144- | 1989 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Mortality | LC50 | 48 | hours | 18 | μg/L | 0.2 ug/L / 12.5 ug/L / 25 ug/L / 50 ug/L / 100 ug/L / 200 ug/L / 400 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 60.92 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 102.5 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 267 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 7.92 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >200～300 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 77.4 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 17.47 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 14.9 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 2.2501 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Farfantepenaeus duorarum | Mortality | LC50 | 96 | hours | 832 | μg/L | 16 ECOTOX | Cripe,G.M. | Comparative Acute Toxicities of Several Pesticides and Metals to Mysidopsis bahia and Postlarval Penaeus duorarum | Environ. Toxicol. Chem.13(11): 1867-1872 | 1994 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 2.139 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 20.97 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 6 | μg/L | 16 ECOTOX | Tsui,M.T.K., W.X. Wang, and L.M. Chu | Influence of Glyphosate and Its Formulation (Roundup) on the Toxicity and Bioavailability of Metals to Ceriodaphnia dubia | Environ. Pollut.138(1): 59-68 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 90.44 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 95.55 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 257 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >300～400 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 38 | μg/L | 16 ECOTOX | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 96 | hours | 10 | μg/L | 16 ECOTOX | Salazar,M.H., and S.M. Salazar | Acute Effects of (bis)Tributyltin Oxide on Marine Organisms | Tech.Rep.No.1299, Naval Ocean Systems Ctr., San Diego, CA:87 p. | 1989 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >107.8～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 24 | hours | 400 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 20.3 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 100 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Survival | NOEC | 12 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Survival | NOEC | 16 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 180 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 5.6 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Tisbe battagliai | Mortality | NOEC | 24 | hours | 0.1 | mg/L | 16 ECOTOX | Macken,A., M. Giltrap, K. Ryall, B. Foley, E. McGovern, B. McHugh, and M. Davoren | A Test Battery Approach to the Ecotoxicological Evaluation of Cadmium and Copper Employing a Battery of Marine Bioassays | Ecotoxicology18(4): 470-480 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 56 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 320 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 180 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 64 | hours | 0.027 | ppm | 16 ECOTOX | Anderson,B.G. | The Apparent Thresholds of Toxicity to Daphnia magna for Chlorides of Various Metals when Added to Lake Erie Water | Trans. Am. Fish. Soc.78:96-113 | 1948 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 180 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Tisbe battagliai | Mortality | NOEC | 48 | hours | 0.05 | mg/L | 16 ECOTOX | Macken,A., M. Giltrap, K. Ryall, B. Foley, E. McGovern, B. McHugh, and M. Davoren | A Test Battery Approach to the Ecotoxicological Evaluation of Cadmium and Copper Employing a Battery of Marine Bioassays | Ecotoxicology18(4): 470-480 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 11.99 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 180 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 5.4 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 10 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Survival | NOEC | 2 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Survival | NOEC | 10 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 56 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 18 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 3.2 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 100 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 100 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 1.8 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 56 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 24 | hours | 10 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 10 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 32 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 196 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-ZERO | 48 | hours | 51.9 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 24 | hours | 135 | μg/L | 0 ug/L / 45 ug/L / 135 ug/L / 270 ug/L | 16 ECOTOX | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-ZERO | 48 | hours | 31.5 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-ZERO | 48 | hours | 81 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-ZERO | 48 | hours | 38.2 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-ZERO | 48 | hours | 1.6 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 48 | hours | 13 | μg/L | 5.1 ug/L / 8.1 ug/L / 13 ug/L / 20 ug/L / 38 ug/L / 77 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 48 | hours | 186 | μg/L | 3.8 ug/L / 83 ug/L / 186 ug/L / 370 ug/L / 711 ug/L / 1370 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-ZERO | 48 | hours | 1.3 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-ZERO | 48 | hours | 1.6 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 1.8 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 6.4 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 56 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 107 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 56 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 81.1 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 210 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | 2021/10/25 | |||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 152 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | 2021/10/25 | |||||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 116 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 107 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 3.7 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 123 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 2.3 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Growth (Length) | NOEL | 24 | hours | 25 | μg/L | 16 ECOTOX | Hunter,K., and G. Pyle | Morphological Responses of Daphnia pulex to Chaoborus americanus Kairomone in the Presence and Absence of Metals | Environ. Toxicol. Chem.23(5): 1311-1316 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Filtration rate | NOEL | 48 | hours | 0.1 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Growth (Size) | NOEL | 15 | days | 60 | μg/L | 16 ECOTOX | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 180 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | NR-LETH | 48 | hours | 4.4 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 36.3 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 10 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 24 | hours | 421 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 78.2 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 42.68 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Americamysis bahia | Mortality | LC50 | 96 | hours | 153 | μg/L | 16 ECOTOX | Cripe,G.M. | Comparative Acute Toxicities of Several Pesticides and Metals to Mysidopsis bahia and Postlarval Penaeus duorarum | Environ. Toxicol. Chem.13(11): 1867-1872 | 1994 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 37.9 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 29.8 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 30 | μg/L | 16 ECOTOX | Adema,D.M.M., and A.M. Degroot-Van Zijl | The Influence of Copper on the Water Flea Daphnia magna (De Invloed van Koper op de Watervlo Daphnia magna) | TNO Nieuws27(9): 474-482 | 1972 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 24 | hours | 398 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 102.5 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | 67.4 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 347 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Tisbe battagliai | Mortality | EC10 | 48 | hours | 0.02 | mg/L | 16 ECOTOX | Macken,A., M. Giltrap, K. Ryall, B. Foley, E. McGovern, B. McHugh, and M. Davoren | A Test Battery Approach to the Ecotoxicological Evaluation of Cadmium and Copper Employing a Battery of Marine Bioassays | Ecotoxicology18(4): 470-480 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Mortality | LC50 | 48 | hours | 18 | μg/L | 16 ECOTOX | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 78.7 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 110.3 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | 108.7 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 10.4 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 131 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 44.1 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >200～300 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | 67.4 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 29.3 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 207 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 31.77 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 180 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 13.5 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 56 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 56 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Growth (Size) | LOEL | 15 | days | 90 | μg/L | 16 ECOTOX | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Filtration rate | LOEL | 48 | hours | 10 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Filtration rate | LOEL | 48 | hours | 1 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Filtration rate | LOEL | 48 | hours | 0.1 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Tisbe battagliai | Mortality | LOEC | 24 | hours | 0.2 | mg/L | 16 ECOTOX | Macken,A., M. Giltrap, K. Ryall, B. Foley, E. McGovern, B. McHugh, and M. Davoren | A Test Battery Approach to the Ecotoxicological Evaluation of Cadmium and Copper Employing a Battery of Marine Bioassays | Ecotoxicology18(4): 470-480 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 16.16 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 1.892 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 12.2 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Tisbe battagliai | Mortality | LOEC | 48 | hours | 0.05 | mg/L | 16 ECOTOX | Macken,A., M. Giltrap, K. Ryall, B. Foley, E. McGovern, B. McHugh, and M. Davoren | A Test Battery Approach to the Ecotoxicological Evaluation of Cadmium and Copper Employing a Battery of Marine Bioassays | Ecotoxicology18(4): 470-480 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～150 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 180 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 32 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 30 | μg/L | 16 ECOTOX | Cairns,M.A., A.V. Nebeker, J.H. Gakstatter, and W.L. Griffis | Toxicity of Copper-Spiked Sediments to Freshwater Invertebrates | Environ. Toxicol. Chem.3(3): 435-445 | 1984 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 77 | μg/L | 16 ECOTOX | Cairns,M.A., A.V. Nebeker, J.H. Gakstatter, and W.L. Griffis | Toxicity of Copper-Spiked Sediments to Freshwater Invertebrates | Environ. Toxicol. Chem.3(3): 435-445 | 1984 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 61.18 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 376 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 76.7 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 26 | μg/L | 16 ECOTOX | Chapman,G.A., S. Ota, and F. Recht | Effects of Water Hardness on the Toxicity of Metals to Daphnia magna | U.S.EPA, Corvallis, OR:17 p. | 1980 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 0.9133 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Nitocra spinipes | Mortality | LC50 | 96 | hours | 2100 | μg/L | 16 ECOTOX | Ytreberg,E., J. Karlsson, and B. Eklund | Comparison of Toxicity and Release Rates of Cu and Zn from Anti-Fouling Paints Leached in Natural and Artificial Brackish Seawater | Sci. Total Environ.408(12): 2459-2466 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 39.5 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 16.93 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 96 | hours | 16.1 | μg/L | 16 ECOTOX | Hunt,J.W., B.S. Anderson, B.M. Phillips, P.N. Nicely, R.S. Tjeerdema, H.M. Puckett, M. Stephenson, K. Worcester, and V. | Ambient Toxicity due to Chlorpyrifos and Diazinon in a Central California Coastal Watershed | Environ. Monit. Assess.82:83-112 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 10 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 14 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 210 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 138 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 97.9 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 91.9 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 230 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 220 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 221 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 1090 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 240 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 81.8 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 50.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 31.7 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 315 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 295 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 15.7 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 124 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 193 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 159 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 932 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 55.4 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 56.5 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 372 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 14.5 | μg/L | 2.3 ug/L / 7.98-10.2 ug/L / 10.8-14.3 ug/L / 30.6 ug/L / 58.4 ug/L / 138 ug/L / 291 ug/L | 16 ECOTOX | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 197 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 97.1 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 41 | μg/L | 16 ECOTOX | Elnabarawy,M.T., A.N. Welter, and R.R. Robideau | Relative Sensitivity of Three Daphnid Species to Selected Organic and Inorganic Chemicals | Environ. Toxicol. Chem.5(4): 393-398 | 1986 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 634 | μg/L | 6.5 ug/L / 50.1-57.5 ug/L / 97.0-114 ug/L / 197-206 ug/L / 322-329 ug/L / 726-743 ug/L / 1730 ug/L | 16 ECOTOX | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 25 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 314 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 10 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 151 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 60.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 93 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 70.8 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 104 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 17 | μg/L | 5.1 ug/L / 8.1 ug/L / 13 ug/L / 20 ug/L / 38 ug/L / 77 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 9.22 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 106 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | EC50 | 48 | hours | >0～50 | μg/L | 16 ECOTOX | Pinho,G.L.L., and A. Bianchini | Acute Copper Toxicity in the Euryhaline Copepod Acartia tonsa: Implications for the Development of an Estuarine and Marine Biotic Ligand Model | Environ. Toxicol. Chem.29(8): 1834-1840 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 296 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 245 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 198 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 241 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 113 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 310 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 20 | nM | 16 ECOTOX | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 638 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 320 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 48 | hours | 15.9 | μg/L | 16 ECOTOX | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 301 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >25～30 | nM | 16 ECOTOX | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >150～200 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >10～15 | nM | 16 ECOTOX | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 304 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 69 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 207 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 128 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 220 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 671 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 21.4 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | EC50 | 48 | hours | >50～100 | μg/L | 16 ECOTOX | Pinho,G.L.L., and A. Bianchini | Acute Copper Toxicity in the Euryhaline Copepod Acartia tonsa: Implications for the Development of an Estuarine and Marine Biotic Ligand Model | Environ. Toxicol. Chem.29(8): 1834-1840 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 308 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 260 | μg/L | 3.8 ug/L / 83 ug/L / 186 ug/L / 370 ug/L / 711 ug/L / 1370 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 87 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 40 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 58.5 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 129 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 129 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Tisbe battagliai | Mortality | EC50 | 24 | hours | 0.19 | mg/L | 16 ECOTOX | Macken,A., M. Giltrap, K. Ryall, B. Foley, E. McGovern, B. McHugh, and M. Davoren | A Test Battery Approach to the Ecotoxicological Evaluation of Cadmium and Copper Employing a Battery of Marine Bioassays | Ecotoxicology18(4): 470-480 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 172 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 25.7 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 22.2 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 47 | μg/L | 16 ECOTOX | Clement,B., and S. Zaid | A New Protocol to Measure the Effects of Toxicants on Daphnid-Algae Interactions | Chemosphere55(10): 1429-1438 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 53.8 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 322 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >30～35 | nM | 16 ECOTOX | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 200 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 191 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 126 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 107 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 354 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 430 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 0.03 | mg/L | 16 ECOTOX | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 108 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 9.8 | μg/L | 16 ECOTOX | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 275 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 354 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 200 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 320 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 275 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 311 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 71 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 106 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 86.6 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 60 | μg/L | 16 ECOTOX | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 81.6 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 343 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 211 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 109 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 221 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 180 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 204 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 221 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 354 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 607 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 281 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 116 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | EC50 | 48 | hours | >50～100 | μg/L | 16 ECOTOX | Pinho,G.L.L., and A. Bianchini | Acute Copper Toxicity in the Euryhaline Copepod Acartia tonsa: Implications for the Development of an Estuarine and Marine Biotic Ligand Model | Environ. Toxicol. Chem.29(8): 1834-1840 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 5.49 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 192 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 76.5 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 542 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 48 | hours | 10.4 | μg/L | 16 ECOTOX | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 7.7 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 333 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 9.2 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 225 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 87.8 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 2.64 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 6.35 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 245 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 7.89 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 24.8 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 21 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 824 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 102 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 369 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 223 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | 41.8 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Immobilization | LC50 | 48 | hours | 56.3 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 104 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 48 | hours | 7.97 | μg/L | 16 ECOTOX | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 356 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 24 | hours | 6 | μg/L | 16 ECOTOX | Tsui,M.T.K., W.X. Wang, and L.M. Chu | Influence of Glyphosate and Its Formulation (Roundup) on the Toxicity and Bioavailability of Metals to Ceriodaphnia dubia | Environ. Pollut.138(1): 59-68 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 149 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Tisbe battagliai | Mortality | EC10 | 24 | hours | 0.07 | mg/L | 16 ECOTOX | Macken,A., M. Giltrap, K. Ryall, B. Foley, E. McGovern, B. McHugh, and M. Davoren | A Test Battery Approach to the Ecotoxicological Evaluation of Cadmium and Copper Employing a Battery of Marine Bioassays | Ecotoxicology18(4): 470-480 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 332 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 292 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 398 | nM | 16 ECOTOX | Canli,M. | Effects of Copper Pre-Exposure Routes on the Energy Reserves and Subsequent Copper Toxicity in Daphnia magna | Environ. Toxicol.21(5): 521-527 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 1.505 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 2.21 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Nitocra spinipes | Mortality | LC25 | 96 | hours | 1200 | μg/L | 16 ECOTOX | Ytreberg,E., J. Karlsson, and B. Eklund | Comparison of Toxicity and Release Rates of Cu and Zn from Anti-Fouling Paints Leached in Natural and Artificial Brackish Seawater | Sci. Total Environ.408(12): 2459-2466 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >108.7～200 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 7.88 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC100 | 48 | hours | 11.6 | μg/L | 16 ECOTOX | Tsui,M.T.K., W.X. Wang, and L.M. Chu | Influence of Glyphosate and Its Formulation (Roundup) on the Toxicity and Bioavailability of Metals to Ceriodaphnia dubia | Environ. Pollut.138(1): 59-68 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 5.38 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 17.7 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 100.9 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 37 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 243 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 212 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 139 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 200 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 175 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 109 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 57.6 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 198 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 204 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 57.28 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 24 | hours | 22 | μg/L | 16 ECOTOX | Sorvari,J., and M. Sillanpaa | Influence of Metal Complex Formation on Heavy Metal and Free EDTA and DTPA Acute Toxicity Determined by Daphnia magna | Chemosphere33(6): 1119-1127 | 1996 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 257 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 236 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 247 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 142 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 34 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 5.62 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >15～20 | nM | 16 ECOTOX | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 222 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 48 | hours | 5.57 | μg/L | 16 ECOTOX | Naddy,R.B., G.R. Stern, and R.W. Gensemer | Effect of Culture Water Hardness on the Sensitivity of Ceriodaphnia dubia to Copper Toxicity | Environ. Toxicol. Chem.22(6): 1269-1271 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 201 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 221 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >200～250 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 251 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 162 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 220 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >250～300 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 251 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 102 | μg/L | 16.8 ug/L / 59-59.4 ug/L / 122-128 ug/L / 258 ug/L / 481 ug/L / 1010 ug/L / 1850 ug/L | 16 ECOTOX | Call,D.J., L.T. Brooke, D.H. Hammermeister, C.E. Northcott, and A.D. Hoffman | Variation of Acute Toxicity with Water Source | Center for Lake Superior Environmental Studies, Report No. LSRI0273:58 p. | 1983 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 64 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 340 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 174 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 415 | μg/L | 0 ug/L / >0-<1000 ug/L | 16 ECOTOX | Rainville,L.C., A.V. Coelho, and D. Sheehan | Application of a Redox-Proteomics Toolbox to Daphnia magna Challenged with Model Pro-Oxidants Copper and Paraquat | Environ. Toxicol. Chem.34(1): 84-91 | 2015 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | LC50 | 48 | hours | 26.2 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality | LC50 | 48 | hours | 0.8478 | μg/L | 16 ECOTOX | ENSR International | Application of the Biotic Ligand Model (BLM): Copper at Selected Locations in the Taunton River Basin in Massachusetts | ENSR Corporation Document 8734-324-100. Massachusetts Department of Environment Protection, Westford, MA:943 p. | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Tisbe battagliai | Mortality | EC50 | 48 | hours | 0.08 | mg/L | 16 ECOTOX | Macken,A., M. Giltrap, K. Ryall, B. Foley, E. McGovern, B. McHugh, and M. Davoren | A Test Battery Approach to the Ecotoxicological Evaluation of Cadmium and Copper Employing a Battery of Marine Bioassays | Ecotoxicology18(4): 470-480 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 261 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., F.M. Vasconcelos, F.M.G. Tack, H.E. Allen, and C.R. Janssen | Effect of Dissolved Organic Matter Source on Acute Copper Toxicity to Daphnia magna | Environ. Toxicol. Chem.23(5): 1248-1255 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | >10～15 | nM | 16 ECOTOX | Bossuyt,B.T., and C.R. Janssen | Influence of Bioavailability on Acclimation of Daphnia magna to Copper | Meded. Fac. Landbouwwet. Univ. Gent67(4): 133-136 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 99 | μg/L | 16 ECOTOX | Kramer,K.J.M., R.G. Jak, B. Van Hattum, R.N. Hooftman, and J.J.G. Zwolsman | Copper Toxicity in Relation to Surface Water-Dissolved Organic Matter: Biological Effects to Daphnia magna | Environ. Toxicol. Chem.23(12): 2971-2980 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Acartia tonsa | Mortality | LC50 | 48 | hours | >300～400 | μg/L | <0.000001 g/L / <0.000001 g/L / 0.02 g/L / 0.2 g/L / 2 g/L | 16 ECOTOX | Monteiro,S.C.R., G.L.L. Pinho, K. Hoffmann, I.F. Barcarolli, and A. Bianchini | Acute Waterborne Copper Toxicity to the Euryhaline Copepod Acartia tonsa at Different Salinities: Influence of Natural Freshwater and Marine Dissolved Organic Matter | Environ. Toxicol. Chem.32(6): 1412-1419 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 290 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 139 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 173 | nM | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | A Biotic Ligand Model Predicting Acute Copper Toxicity for Daphnia magna: The Effects of Calcium, Magnesium, Sodium, Potassium, and pH | Environ. Sci. Technol.36(1): 48-54 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Immobilization | EC50 | 48 | hours | 31 | μg/L | 16 ECOTOX | Elnabarawy,M.T., A.N. Welter, and R.R. Robideau | Relative Sensitivity of Three Daphnid Species to Selected Organic and Inorganic Chemicals | Environ. Toxicol. Chem.5(4): 393-398 | 1986 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Immobilization | EC50 | 48 | hours | 26.3 | μg/L | 16 ECOTOX | Gensemer,R.W., R.B. Naddy, W.A. Stubblefield, J.R. Hockett, R. Santore, and P. Paquin | Evaluating the Role of Ion Composition on the Toxicity of Copper to Ceriodaphnia dubia in very Hard Waters | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.133(1-2): 87-97 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | LETHAL | EC50 | 2 | days | 0.014 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Nebeker ea 86 | 2017/03/01 | |||||||||
| 甲殻類 | Daphnia magna | LETHAL | EC50 | 2 | days | 0.0088 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Curtis and Ward 81 | 2017/03/01 | |||||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 49 | hours | 680 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea virginica | Abnormal development | EC10 | 48 | hours | 12.3 | ppb | 16 ECOTOX | MacInnes,J.R. | Response of Embryos of the American Oyster, Crassostrea virginica, to Heavy Metal Mixtures | Mar. Environ. Res.4(3): 217-227 | 1981 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Valve closure | EC50 | 48 | hours | 2.1 | μM | 16 ECOTOX | Curtis,T.M., R. Williamson, and M.H. Depledge | Simultaneous, Long-Term Monitoring of Valve and Cardiac Activity in the Blue Mussel Mytilus edulis Exposed to Copper | Mar. Biol.136(5): 837-846 | 2000 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus droebachiensis | Developmental changes | EC50 | 120 | hours | 21 | μg/L | 16 ECOTOX | Dinnel,P.A., J.M. Link, Q.J. Stober, M.W. Letourneau, and W.E. Roberts | Comparative Sensitivity of Sea Urchin Sperm Bioassays to Metals and Pesticides | Arch. Environ. Contam. Toxicol.18(5): 748-755 | 1989 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus purpuratus | Developmental changes | EC50 | 120 | hours | 6.3 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Dendraster excentricus | Developmental changes | EC50 | 72 | hours | 33 | μg/L | 16 ECOTOX | Dinnel,P.A., J.M. Link, Q.J. Stober, M.W. Letourneau, and W.E. Roberts | Comparative Sensitivity of Sea Urchin Sperm Bioassays to Metals and Pesticides | Arch. Environ. Contam. Toxicol.18(5): 748-755 | 1989 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus purpuratus | Developmental changes | EC50 | 120 | hours | 6.3 | μg/L | 16 ECOTOX | Dinnel,P.A., J.M. Link, Q.J. Stober, M.W. Letourneau, and W.E. Roberts | Comparative Sensitivity of Sea Urchin Sperm Bioassays to Metals and Pesticides | Arch. Environ. Contam. Toxicol.18(5): 748-755 | 1989 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus droebachiensis | Developmental changes | EC50 | 120 | hours | 21.3 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Chironomus riparius | Mortality | LC50 | 96 | hours | 0.043 | mg/L | 16 ECOTOX | Milani,D., T.B. Reynoldson, U. Borgmann, and J. Kolasa | The Relative Sensitivity of Four Benthic Invertebrates to Metals in Spiked-Sediment Exposures and Application to Contaminated Field Sediment | Environ. Toxicol. Chem.22(4): 845-854 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 24 | hours | 680 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Chironomus riparius | Survival | LC50 | 10 | days | 0.07 | mg/L | 16 ECOTOX | Milani,D., T.B. Reynoldson, U. Borgmann, and J. Kolasa | The Relative Sensitivity of Four Benthic Invertebrates to Metals in Spiked-Sediment Exposures and Application to Contaminated Field Sediment | Environ. Toxicol. Chem.22(4): 845-854 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Chironomus tentans | Mortality | LC50 | 10 | days | 38 | μg/L | 16 ECOTOX | Cairns,M.A., A.V. Nebeker, J.H. Gakstatter, and W.L. Griffis | Toxicity of Copper-Spiked Sediments to Freshwater Invertebrates | Environ. Toxicol. Chem.3(3): 435-445 | 1984 | 2022/01/25 | ||||||
| 甲殻類 | Chironomus tentans | Mortality | LC50 | 10 | days | 249 | μg/L | 16 ECOTOX | Cairns,M.A., A.V. Nebeker, J.H. Gakstatter, and W.L. Griffis | Toxicity of Copper-Spiked Sediments to Freshwater Invertebrates | Environ. Toxicol. Chem.3(3): 435-445 | 1984 | 2022/01/25 | ||||||
| 甲殻類 | Chironomus riparius | Survival | LC25 | 10 | days | 0.041 | mg/L | 16 ECOTOX | Milani,D., T.B. Reynoldson, U. Borgmann, and J. Kolasa | The Relative Sensitivity of Four Benthic Invertebrates to Metals in Spiked-Sediment Exposures and Application to Contaminated Field Sediment | Environ. Toxicol. Chem.22(4): 845-854 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Chironomus riparius | Growth | IC25 | 10 | days | 0.024 | mg/L | 16 ECOTOX | Milani,D., T.B. Reynoldson, U. Borgmann, and J. Kolasa | The Relative Sensitivity of Four Benthic Invertebrates to Metals in Spiked-Sediment Exposures and Application to Contaminated Field Sediment | Environ. Toxicol. Chem.22(4): 845-854 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Chironomus riparius | Mortality | NR-ZERO | 96 | hours | 35 | μg/L | 16 ECOTOX | Stuijfzand,S.C., M.J. Jonker, E. Van Ammelrooy, and W. Admiraal | Species-Specific Responses to Metals in Organically Enriched River Water, with Emphasis on Effects of Humic Acids | Environ. Pollut.106(1): 115-121 | 1999 | 2022/01/25 | ||||||
| 甲殻類 | Dendraster excentricus | Developmental changes | EC50 | 72 | hours | 33.3 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 59 | hours | 580 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Mortality | LC50 | 4 | days | 80 | μg/L | 16 ECOTOX | Watling,H.R. | Comparative Study of the Effects of Zinc, Cadmium, and Copper on the Larval Growth of Three Oyster Species | Bull. Environ. Contam. Toxicol.28:195-201 | 1982 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Mortality | LC50 | 48 | hours | 12 | μg/L | 16 ECOTOX | Harrison,F.L., J.P. Knezovich, and J.S. Tucker | The Sensitivity of Embryos of the Pacific Oyster Crassostrea gigas to Different Chemical Forms of Copper | Technical Report UCRL-52725, Lawrence Livermore National Lab., CA:30 p. | 1981 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea virginica | Mortality | LC50 | 12 | days | 32.8 | μg/L | 16 ECOTOX | Calabrese,A., J.R. MacInnes, D.A. Nelson, and J.E. Miller | Survival and Growth of Bivalve Larvae Under Heavy-Metal Stress | Mar. Biol.41:179-184 | 1977 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea virginica | Developmental changes | EC50 | 48 | hours | 15.1 | μg/L | 16 ECOTOX | MacInnes,J.R., and A. Calabrese | Response of Embryos of the American Oyster, Crassostrea virginica, to Heavy Metals at Different Temperatures | In: D.S.McLusky, and A.J.Berry (Eds.), Physiology and Behaviour of Marine Organisms, Permagon Press, New York, NY:195-202 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Mortality | LC50 | 4 | days | 100 | μg/L | 16 ECOTOX | Watling,H.R. | Comparative Study of the Effects of Zinc, Cadmium, and Copper on the Larval Growth of Three Oyster Species | Bull. Environ. Contam. Toxicol.28:195-201 | 1982 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Mortality | LC100 | 48 | hours | 20 | μg/L | 16 ECOTOX | Harrison,F.L., J.P. Knezovich, and J.S. Tucker | The Sensitivity of Embryos of the Pacific Oyster Crassostrea gigas to Different Chemical Forms of Copper | Technical Report UCRL-52725, Lawrence Livermore National Lab., CA:30 p. | 1981 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 96 | hours | 430 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea virginica | Developmental changes | EC50 | 48 | hours | 18.7 | μg/L | 16 ECOTOX | MacInnes,J.R., and A. Calabrese | Response of Embryos of the American Oyster, Crassostrea virginica, to Heavy Metals at Different Temperatures | In: D.S.McLusky, and A.J.Berry (Eds.), Physiology and Behaviour of Marine Organisms, Permagon Press, New York, NY:195-202 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 64 | hours | 580 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 12 | hours | 1050 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Mytilus edulis | Slowed, Retarded, Delayed or Non-development | EC50 | 48 | hours | 84 | μg/L | 16 ECOTOX | Ross,K.E., and J.R. Bidwell | A 48-h Larval Development Toxicity Test Using the Marine Polychaete Galeolaria caespitosa Lamarck (Fam. Serpulidae) | Arch. Environ. Contam. Toxicol.40(4): 489-496 | 2001 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Growth (Delayed), general | EC50 | 4 | days | 50 | μg/L | 16 ECOTOX | Watling,H.R. | Comparative Study of the Effects of Zinc, Cadmium, and Copper on the Larval Growth of Three Oyster Species | Bull. Environ. Contam. Toxicol.28:195-201 | 1982 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 48 | hours | 650 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Growth (Delayed), general | EC50 | 4 | days | 75 | μg/L | 16 ECOTOX | Watling,H.R. | Comparative Study of the Effects of Zinc, Cadmium, and Copper on the Larval Growth of Three Oyster Species | Bull. Environ. Contam. Toxicol.28:195-201 | 1982 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea virginica | Mortality | LC50 | 48 | hours | 103 | μg/L | 16 ECOTOX | Calabrese,A., R.S. Collier, D.A. Nelson, and J.R. MacInnes | The Toxicity of Heavy Metals to Embryos of the American Oyster Crassostrea virginica | Mar. Biol.18(3): 162-166 | 1973 | 2022/01/25 | ||||||
| 甲殻類 | Mercenaria mercenaria | Growth | EC50 | 168 | hours | 37.6 | μg/L | 16 ECOTOX | Keppler,C.J., and A.H. Ringwood | Effects of Metal Exposures on Juvenile Clams, Mercenaria mercenaria | Bull. Environ. Contam. Toxicol.68(1): 43-48 | 2002 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea virginica | Developmental changes | EC50 | 48 | hours | 18.3 | μg/L | 16 ECOTOX | MacInnes,J.R., and A. Calabrese | Response of Embryos of the American Oyster, Crassostrea virginica, to Heavy Metals at Different Temperatures | In: D.S.McLusky, and A.J.Berry (Eds.), Physiology and Behaviour of Marine Organisms, Permagon Press, New York, NY:195-202 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Mortality | LC50 | 48 | hours | 12 | μg/L | 16 ECOTOX | Knezovich,J.P., F.L. Harrison, and J.S. Tucker | The Influence of Organic Chelators on the Toxicity of Copper to Embryos of the Pacific Oyster, Crassostrea gigas | Arch. Environ. Contam. Toxicol.10(2): 241-249 | 1981 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Developmental changes | EC50 | 48 | hours | 6.1 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 95 | hours | 310 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 388 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 200 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 106 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 229 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 35 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Crassostrea gigas | Immobilization | EC50 | 18 | hours | 1050 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | Copper Sensitivity of Adult Pacific Oysters | In: J.H.Thorp and J.W.Gibbons (Eds.), Dep.Energy Symp.Ser., Energy and Environmental Stress in Aquatic Systems, Augusta, GA48:301-315 | 1978 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 526 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 826 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 136 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 157 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 244 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 9.8 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 60 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 51 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 92.6 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 292 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31.8 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 1213 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 50 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 58 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 30 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 63 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 421 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 42 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 39 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 289 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 300 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 91 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 31 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 33.8 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 37.9 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 529 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 93 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 792 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 40.9 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 648 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 332 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 295 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 686 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 84 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 8.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 42 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 36 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 5.5 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 4.9 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 34 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 33 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 32 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 2.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 25.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 21.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 7.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 27 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 399 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 188 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 257 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 23 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 19.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 4.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 28.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 6.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 465 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Ryan, A.C. et al. | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model. | Environ Toxicol Chem., 23(6):1567-74 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 366 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 25 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 134.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 172.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 14.74 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 31.65 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 141.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 308 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Grosell, M. et al. | Physiology is pivotal for interactions between salinity and acute copper toxicity to fish and invertebrates | Aquat Toxicol. 2007; 84(2):162-72 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 10.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 208 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L [meas. (geom. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L [meas. (geom. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L [meas. (geom. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 8.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 220 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11, 1079-1083 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 117 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 109 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC50 | 48 | hours | 157 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 798 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Erikson, R.J. et al. | The effects of water chemistry on the toxicity of copper to fathead minnows | Environ Toxicol Chem., 15, 181-193. | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 7.2 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 207 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Scudder, B. et al. | Effects of Copper on Development of the Fathead Minnow, Pimephales promelas | Aquatic Toxicology. 12, 107-124 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 37.78 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 322 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11, 1079-1083 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 30 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 304 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11, 1079-1083 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 292 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 354 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 9.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 170 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 9.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 151 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11, 1079-1083 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 70 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 69 | μg/L [meas. (geom. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 5.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. et al. | Effects of Diet, Water Hardness and Population Source on Acute and Chronic Copper Toxicity to Ceriodaphnia dubia | Arch. Environ. Contam. Toxicol. 18, 601-611 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 2.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | van Leeuwen, C.J. et al. | Intermittent Flow System for Population Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol. 40, 496-502 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 9.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | van Leeuwen, C.J. et al. | Intermittent Flow System for Population Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol. 40, 496-502 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 3.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | van Leeuwen, C.J. et al. | Intermittent Flow System for Population Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol. 40, 496-502 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | LaBreche, T.M.C. et al. | Copper Toxicity to Larval Mercenaria mercenaria (hard clam) | Environ Toxicol Chem., 21 (4), 760-766 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 40 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 0.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 90 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 380 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 14 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 52 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 56 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 10 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 20.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 76 | μg/L [meas. (geom. mean) element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 200 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 43 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 44 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 1.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. et al. | Effects of Diet, Water Hardness and Population Source on Acute and Chronic Copper Toxicity to Ceriodaphnia dubia | Arch. Environ. Contam. Toxicol. 18, 601-611 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 44.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 66 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 58.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 29.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 78.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 26.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC50 | 48 | hours | 267 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC50 | 48 | hours | 30 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 71 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 106.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 18.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 22.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 15.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 16.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 21.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 87 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 69 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Taylor, E.J. et al. | Evaluation of a Chronic Toxicity Test Using Growth of the Insect Chironomus riparius Meigen | In. Bioindicators and Environmental Management. Eds Jeffrey, D.W. & Madden. Academic Press, p343-352 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 99 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 19.28 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 93 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 638 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 124 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 109 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 40 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 34 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 25 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 21 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 31 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 100 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 177 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 157 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 53.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 104 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 17.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 42.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 108.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 7.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 159 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Heijerick DG, Janssen CR | Comparison of the effect of different pH buffering techniques on the toxicity of copper and zinc to Daphnia magna and Pseudokirchneriella subcapitata | Ecotoxicology 13:697-705 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 14.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 192 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 86.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 101.8 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 34.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 21 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 50 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 4.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 7.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 130.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 29.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 50.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 275 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 607 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 60.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 212 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 81.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 128 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | >295 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 129 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 261 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 3.8 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 276 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 19.24 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 6.18 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 6.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | <13 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 68.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 19.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 14.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 67.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 21.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 14.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 9.46 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 20 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 24.43 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Yim JH, Kim KW, Kim SD | Effect of hardness on acute toxicity of metal mixtures using Daphnia magna: prediction of acid mine drainage toxicity | Journal of Hazardous Materials B138:16-21 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 35.2 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 119 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 175 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 484 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 281 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 178 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 7.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 14 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | ||||||||||||
| 甲殻類 | Daphnia magna | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | ||||||||||||
| 甲殻類 | Daphnia magna | 12 ECHA Information on Registered Substances | 2 | Adam N, Vakurov A, Knapen D, Blust R | The chronic toxicity of CuO nanoparticles and copper salt to Daphnia magna | Journal of Hazardous materials 283:416-422 | 2021/10/25 | ||||||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 22 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 2 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 122.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 8.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 24.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 257 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 29.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 79.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 10.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 96 | hours | 5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Johnson BM, Chao MM, Tedrow OR, McQueen AD, Rodgers JH Jr. | Responses of Lepomis macrochirus, Pimephales promelas, Hyalella azteca, Ceriodaphnia dubia, and Daphnia magna to exposures of Algimycin PWF and copper sulfate pentahydrate | Journal of Aquatic Plant Management 46:176-183 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 12 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 3.98 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 2 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 187.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Heijerick DG, Janssen CR | Comparison of the effect of different pH buffering techniques on the toxicity of copper and zinc to Daphnia magna and Pseudokirchneriella subcapitata | Ecotoxicology 13:697-705 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 10 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 11.1 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 2 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 2.8 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 4.8 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 2 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 7.4 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 6.5 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 10.14 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 6.03 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Johnson BM, Chao MM, Tedrow OR, McQueen AD, Rodgers JH Jr. | Responses of Lepomis macrochirus, Pimephales promelas, Hyalella azteca, Ceriodaphnia dubia, and Daphnia magna to exposures of Algimycin PWF and copper sulfate pentahydrate | Journal of Aquatic Plant Management 46:176-183 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 15.58 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Yim JH, Kim KW, Kim SD | Effect of hardness on acute toxicity of metal mixtures using Daphnia magna: prediction of acid mine drainage toxicity | Journal of Hazardous Materials B138:16-21 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 14 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 44 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 7.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 155.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 96.23 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 68.45 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 81.06 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 61.82 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | >184.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 135.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 35.23 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 68.31 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 87.39 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 32 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 116.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 11 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 12 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 332 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 9 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 311 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 6.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC50 | 48 | hours | 147 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 9.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 11.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 18 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 23 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 2.2 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 118.5 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 77.3 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 11.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 19 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 39 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 47 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 314 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 430 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 53.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 40.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | <32.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 1.6 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 73 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 1.6 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 2.8 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 6.5 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 16 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 11 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 23 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 42 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 32 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 30 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 1.6 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 100 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 125.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 16.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 235.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | <5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 50 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 24 | hours | 23.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 24 | hours | 12 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 8.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 25.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 25.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 60 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 206 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 45.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 96 | hours | 42 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 302 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 23.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 148 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 17.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 77.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 279 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC50 | 48 | hours | >111 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC50 | 48 | hours | 25 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 372 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 542 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 47.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 29.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 207 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 5.38 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Cooper NL, Bidwell JR, Kumar A | Toxicity of copper, lead, and zinc mixtures to Ceriodaphnia dubia and Daphnia carinata | Ecotoxicology and Environmental Safety 72:1523-1528 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 5.02 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 36.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 239.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 156.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 131 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 37 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 8.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 100 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 56.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 72 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 88.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 104.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 109.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 30.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 78.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 10.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 25.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 60.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia hyalina | LC50 | 48 | hours | 5 | μg/L | 10 EHC (Environmental Health Criteria) | Baudouin MF & Scoppa P | Acute toxicity of various metals to freshwater zooplankton | Bull Environ Contam Toxicol, 12(6) | 2022/01/18 | ||||||||
| 甲殻類 | Chironomus dilutus | LC50 | 96 | hours | 1690 | μg/L | 10 EHC (Environmental Health Criteria) | Nebeker AV, Cairns MA, & Wise CM | Relative sensitivity of Chironomus tentans life stages to copper | Environ Toxicol Chem, 3 | 2022/01/18 | ||||||||
| 甲殻類 | Chironomus riparius | LC50 | 48 | hours | 1200 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Taylor EJ, Maund SJ, & Pascoe D | Toxicity of four common pollutants to the freshwater macroinvertebrates Chironomus riparius Meigen (Insecta: Diptera) and Gammarus pulex (L.) (Crustacea: Amphipoda) | Arch Environ Contam Toxicol, 21 | 2022/01/18 | |||||||
| 甲殻類 | Chironomus riparius | LC50 | 96 | hours | 700 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Taylor EJ, Maund SJ, & Pascoe D | Toxicity of four common pollutants to the freshwater macroinvertebrates Chironomus riparius Meigen (Insecta: Diptera) and Gammarus pulex (L.) (Crustacea: Amphipoda) | Arch Environ Contam Toxicol, 21 | 2022/01/18 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 0.014 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Nebeker AV, Cairns MA, Onjukka ST, Titus RH | Effect of age on sensitivity of Daphnia magna to cadmium, copper and cyanazine | Environ Toxicol Chem 5 | 2022/01/24 | |||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 0.0088 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Nebeker AV, Cairns MA, Onjukka ST, Titus RH | Effect of age on sensitivity of Daphnia magna to cadmium, copper and cyanazine | Environ Toxicol Chem 5 | 2022/01/24 | |||||||
| 甲殻類 | Ceriodaphnia dubia | LC50 | 48 | hours | 34～37 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Belanger SE, Farris JL, & Cherry DS | Effects of diet, water hardness, and population source on acute and chronic copper toxicity to Ceriodaphnia dubia | Arch Environ Contam Toxicol, 18 | 2022/01/18 | |||||||
| 甲殻類 | Ceriodaphnia dubia | LC50 | 48 | hours | 67 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Belanger SE, Farris JL, & Cherry DS | Effects of diet, water hardness, and population source on acute and chronic copper toxicity to Ceriodaphnia dubia | Arch Environ Contam Toxicol, 18 | 2022/01/18 | |||||||
| 甲殻類 | Chironomus dilutus | LC50 | 96 | hours | 1446 | μg/L | 10 EHC (Environmental Health Criteria) | Nebeker AV, Cairns MA, & Wise CM | Relative sensitivity of Chironomus tentans life stages to copper | Environ Toxicol Chem, 3 | 2022/01/18 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | LC50 | 48 | hours | 13.4 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Oris JT, Winner RW, & Moore MV | A four-day survival and reproduction toxicity test for Ceriodaphnia dubia | Environ Toxicol Chem, 10 | 2022/02/08 | |||||||
| 甲殻類 | Chironomus dilutus | EC50 | 96 | hours | 36.5 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Gauss JD, Woods PE, Winner RW, & Skillings JH | Acute toxicity of copper to three life stages of Chironomus tentans as affected by water hardness-alkalinity | Environ Pollut, A37 | 2022/02/08 | |||||||
| 甲殻類 | Daphnia magna | LC50 | 24 | hours | 380 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Ferrando MD, Andreu-Moliner E, & Fernández-Casalderrey A | Relative sensitivity of Daphnia magna and Brachionus calyciflorus to five pesticides calyciflorus to five pesticides | J Environ Sci Health, B27(5) | 2022/02/08 | |||||||
| 甲殻類 | Ceriodaphnia dubia | LC50 | 48 | hours | 17～32 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Belanger SE, Farris JL, & Cherry DS | Effects of diet, water hardness, and population source on acute and chronic copper toxicity to Ceriodaphnia dubia | Arch Environ Contam Toxicol, 18 | 2022/01/18 | |||||||
| 甲殻類 | Chironomus dilutus | LC50 | 96 | hours | 773 | μg/L | 10 EHC (Environmental Health Criteria) | Nebeker AV, Cairns MA, & Wise CM | Relative sensitivity of Chironomus tentans life stages to copper | Environ Toxicol Chem, 3 | 2022/01/18 | ||||||||
| 甲殻類 | Chironomus dilutus | LC50 | 96 | hours | 298 | μg/L | 10 EHC (Environmental Health Criteria) | Nebeker AV, Cairns MA, & Wise CM | Relative sensitivity of Chironomus tentans life stages to copper | Environ Toxicol Chem, 3 | 2022/01/18 | ||||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 9.8 | μg/L | 10 EHC (Environmental Health Criteria) | Biesinger KE & Christensen GM | Effects of various metals on survival, growth, reproduction, and metabolism of Daphnia magna | J Fish Res Board Can, 29 | 2022/01/18 | ||||||||
| 甲殻類 | Chironomus dilutus | EC50 | 96 | hours | 211 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Gauss JD, Woods PE, Winner RW, & Skillings JH | Acute toxicity of copper to three life stages of Chironomus tentans as affected by water hardness-alkalinity | Environ Pollut, A37 | 2022/02/08 | |||||||
| 甲殻類 | Chironomus dilutus | EC50 | 96 | hours | 977 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Gauss JD, Woods PE, Winner RW, & Skillings JH | Acute toxicity of copper to three life stages of Chironomus tentans as affected by water hardness-alkalinity | Environ Pollut, A37 | 2022/02/08 | |||||||
| 甲殻類 | Chironomus dilutus | EC50 | 96 | hours | 16.7 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Gauss JD, Woods PE, Winner RW, & Skillings JH | Acute toxicity of copper to three life stages of Chironomus tentans as affected by water hardness-alkalinity | Environ Pollut, A37 | 2022/02/08 | |||||||
| 甲殻類 | Chironomus dilutus | EC50 | 48 | hours | 327 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Khangarot BS & Ray PK | Sensitivity of midge larvae of Chironomus tentans Fabricius (Diptera Chironomidae) to heavy metals | Bull Environ Contam Toxicol, 42 | 2022/02/08 | |||||||
| 甲殻類 | Ceriodaphnia reticulata | LC50 | 48 | hours | 17 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mount DI & Norberg TJ | A seven-day life-cycle cladoceran toxicity test | Environ. Toxicol Chem, 3 | 2022/01/18 | |||||||
| 甲殻類 | Ceriodaphnia dubia | LC50 | 48 | hours | 200 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Schubauer-Berigan MK, Dierkes JR, Monson PD & Ankley GT | pH-dependent toxicity of Cd, Cu, Ni and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus | Environ Toxicol Chem, 12 | 2022/01/18 | |||||||
| 甲殻類 | Ceriodaphnia dubia | LC50 | 48 | hours | 28 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Schubauer-Berigan MK, Dierkes JR, Monson PD & Ankley GT | pH-dependent toxicity of Cd, Cu, Ni and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus | Environ Toxicol Chem, 12 | 2022/01/18 | |||||||
| 甲殻類 | Daphnia lumholtzi | LC50 | 96 | hours | 9.4 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Vardia HK, Rao PS, & Durve VS | Effect of copper, cadmium and zinc on fish-food organisms, Daphnia lumholtzi and Cypris subglobosa | Proc Indian Acad Sci (Anim Sci), 97(2) | 2022/01/18 | |||||||
| 甲殻類 | Ceriodaphnia dubia | LC50 | 48 | hours | 9.5 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Schubauer-Berigan MK, Dierkes JR, Monson PD & Ankley GT | pH-dependent toxicity of Cd, Cu, Ni and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus | Environ Toxicol Chem, 12 | 2022/01/18 | |||||||
| 甲殻類 | Ceriodaphnia dubia | LC50 | 48 | hours | 78～81 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Belanger SE, Farris JL, & Cherry DS | Effects of diet, water hardness, and population source on acute and chronic copper toxicity to Ceriodaphnia dubia | Arch Environ Contam Toxicol, 18 | 2022/01/18 | |||||||
| 甲殻類 | Chironomus dilutus | EC50 | 96 | hours | 1184 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Gauss JD, Woods PE, Winner RW, & Skillings JH | Acute toxicity of copper to three life stages of Chironomus tentans as affected by water hardness-alkalinity | Environ Pollut, A37 | 2022/02/08 | |||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 54 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mount DI & Norberg TJ | A seven-day life-cycle cladoceran toxicity test | Environ. Toxicol Chem, 3 | 2022/01/18 | |||||||
| 甲殻類 | Palaemonetes pugio | LC50 | 96 | hours | 3700 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Curtis MW, Copeland TL, & Ward CH | Acute toxicity of 12 industrial chemicals to freshwater and saltwater organisms | Water Res, 13 | 2022/01/18 | |||||||
| 甲殻類 | Palaemonetes pugio | LC50 | 48 | hours | 2100 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Burton DT & Fisher DJ | Acute toxicity of cadmium, copper, zinc, ammonia, 3,3'-dichlorobenzidine, 2,6-dichloro-4-nitroaniline, methylene chloride, and 2,4,6-trichlorophenol to juvenile grass shrimp and killifish | Bull Environ Contam Toxicol, 44 | 2022/01/24 | |||||||
| 甲殻類 | Holmesimysis costata | LC50 | 96 | hours | 17 | μg/L | 10 EHC (Environmental Health Criteria) | Martin M, Hunt JW, Anderson BS, Turpen SL, & Palmer FH | Experimental evaluation of the mysid Holmesimysis costata as a test organism for effluent toxicity testing | Environ Toxicol Chem, 8 | 2022/01/18 | ||||||||
| 甲殻類 | Tisbe battagliai | LC50 | 96 | hours | 88 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Hutchinson TH, Williams TD, & Eales GJ | Toxicity of cadmium, hexavalent chromium and copper to marine fish larvae (Cyprinodon variegatus) and copepods (Tisbe battagliai) | Mar Environ Res, 38 | 2022/01/18 | |||||||
| 甲殻類 | Tisbe battagliai | LC50 | 96 | hours | 64 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Hutchinson TH, Williams TD, & Eales GJ | Toxicity of cadmium, hexavalent chromium and copper to marine fish larvae (Cyprinodon variegatus) and copepods (Tisbe battagliai) | Mar Environ Res, 38 | 2022/01/18 | |||||||
| 甲殻類 | Daphnia ambigua | LC50 | 48 | hours | 54.6 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Vardia HK, Rao PS, & Durve VS | Effect of copper, cadmium and zinc on fish-food organisms, Daphnia lumholtzi and Cypris subglobosa | Proc Indian Acad Sci (Anim Sci), 97(2) | 2022/01/18 | |||||||
| 甲殻類 | Daphnia ambigua | LC50 | 72 | hours | 67.7 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Winner RW & Farrell MP | Acute and chronic toxicity of copper to four species of Daphnia | J Fish Res Board Can, 33 | 2022/02/08 | |||||||
| 甲殻類 | Daphnia parvula | LC50 | 72 | hours | 72 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Winner RW & Farrell MP | Acute and chronic toxicity of copper to four species of Daphnia | J Fish Res Board Can, 33 | 2022/02/08 | |||||||
| 甲殻類 | Daphnia pulex | LC50 | 72 | hours | 86 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Winner RW & Farrell MP | Acute and chronic toxicity of copper to four species of Daphnia | J Fish Res Board Can, 33 | 2022/02/08 | |||||||
| 甲殻類 | Chironomus dilutus | EC50 | 96 | hours | 98.2 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Gauss JD, Woods PE, Winner RW, & Skillings JH | Acute toxicity of copper to three life stages of Chironomus tentans as affected by water hardness-alkalinity | Environ Pollut, A37 | 2022/02/08 | |||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 53 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mount DI & Norberg TJ | A seven-day life-cycle cladoceran toxicity test | Environ. Toxicol Chem, 3 | 2022/01/18 | |||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 45 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Oikari A, Kukkonen J, & Virtanen V | Acute toxicity of chemicals to Daphnia magna in humic waters | Sci Total Environ, 117/118 | 2022/02/08 | |||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 7 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Oikari A, Kukkonen J, & Virtanen V | Acute toxicity of chemicals to Daphnia magna in humic waters | Sci Total Environ, 117/118 | 2022/02/08 | |||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 60 | μg/L | 10 EHC (Environmental Health Criteria) | Biesinger KE & Christensen GM | Effects of various metals on survival, growth, reproduction, and metabolism of Daphnia magna | J Fish Res Board Can, 29 | 2022/01/18 | ||||||||
| 甲殻類 | Daphnia magna | LC50 | 72 | hours | 86.5 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Winner RW & Farrell MP | Acute and chronic toxicity of copper to four species of Daphnia | J Fish Res Board Can, 33 | 2022/02/08 | |||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 23～27 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | LeBlanc GA | Laboratory investigation into the development of resistance of Daphnia magna (Straus) to environmental pollutants | Environ Pollut, A27 | 2022/02/08 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Survival | LOEL | 7 | days | 74.7 | μg/g | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | LOEL | 15 | days | 60 | μg/L | 16 ECOTOX | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 25 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 1 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Survival | LC50 | 7 | days | 7.5 | ng/d | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 25 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEC | 14 | days | 0.01 | mg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEC | 40 | days | 1 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEC | 14 | days | 130 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 55.6 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 14 | days | 86 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 1 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Reproduction/Progeny counts/numbers | NOEL | 24 | hours | 25 | μg/L | 16 ECOTOX | Hunter,K., and G. Pyle | Morphological Responses of Daphnia pulex to Chaoborus americanus Kairomone in the Presence and Absence of Metals | Environ. Toxicol. Chem.23(5): 1311-1316 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 179 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEC | 21 | days | 92.5 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 14 | days | 90 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Reproduction | NOEC | 21 | days | 0.4 | μg/L | 16 ECOTOX | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 12 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Growth (Weight) | NOEL | 21 | days | 183 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 125 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 81.2 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 125 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Survival | EC50 | 7 | days | 7.5 | ng/d | 16 ECOTOX | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Intrinsic rate of increase | NOEL | 15 | days | 60 | μg/L | 16 ECOTOX | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction/Progeny counts/numbers | NOEL | 7 | days | >0～15.9 | μg/g | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Survival | NOEL | 7 | days | >0～20 | μg/g | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Survival | EC50 | 7 | days | 70.5 | μg/g | 16 ECOTOX | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction/Progeny counts/numbers | IC25 | 7 | days | 14.4 | μg/g | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Reproduction/Progeny counts/numbers | NOEC | 12 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEL | 15 | days | 30 | μg/L | 16 ECOTOX | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 35 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEC | 21 | days | 96.2 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Population change (change in N/change in time) | EC50 | 21 | days | 16.1 | μg/L | 16 ECOTOX | Van Leeuwen,C.J., J.L. Buchner, and H. Van Dijk | Intermittent Flow System for Population Toxicity Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol.40(4): 496-502 | 1988 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 35 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 78.8 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 0.015 | mg/L | 16 ECOTOX | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Growth (Dry weight) | NOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction/Progeny counts/numbers | IC50 | 7 | days | 45.3 | μg/g | 16 ECOTOX | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 125 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 125 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEC | 14 | days | 0.01 | mg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | NOEC | 14 | days | 75 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 24～48 | μg | 16 ECOTOX | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 125 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 25 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 125 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 100 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 125 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction/Progeny counts/numbers | IC50 | 7 | days | 5.3 | ng/d | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction/Progeny counts/numbers | IC50 | 7 | days | 45.3 | μg/g | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction/Progeny counts/numbers | IC50 | 7 | days | 5.3 | ng/d | 16 ECOTOX | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY:161 p. | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-LETH | 21 | days | 125 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction/Progeny counts/numbers | IC25 | 7 | days | 2.5 | ng/d | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | NR-ZERO | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Mortality | LOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia cornuta | Reproduction/Time to first progeny | LOEC | 2.61 | days | 0.0000032 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Growth rate | LOEC | 21 | days | 5.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Reproduction/Progeny counts/numbers | LOEC | 21 | days | 229.9 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | growth rate | LOEC | 21 | days | 156.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | LOEC | 21 | days | 5.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Reproduction/Time to first progeny | LOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | growth rate | LOEC | 21 | days | 9.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 61 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Growth rate | LOEC | 21 | days | 5.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 70.5 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | LOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Reproduction/Time to first progeny | LOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LOEC | 21 | days | 156.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | LOEC | 21 | days | 21.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | growth rate | LOEC | 21 | days | 42.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Reproduction/Time to first progeny | LOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | growth rate | EC50 | 21 | days | 88 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 57.1 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | EC50 | 21 | days | 80 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | EC50 | 21 | days | 80 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | EC50 | 21 | days | 85 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | EC50 | 21 | days | 87 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | EC50 | 21 | days | 72 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 35 | μg/L | 16 ECOTOX | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 74.6 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | growth rate | LOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 50.2 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia cornuta | Growth rate | LOEC | 21 | days | 0.0000032 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 56.2 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 71.3 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 56.1 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Reproduction/Time to first progeny | LOEC | 21 | days | 156.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | LOEC | 21 | days | 229.9 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia cornuta | Generation time | LOEC | 33 | days | 0.0000032 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 53.8 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 38.7 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 72.7 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Growth rate | LOEC | 21 | days | 5.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | growth rate | NOEC | 21 | days | 5.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Reproduction/Time to first progeny | NOEC | 21 | days | 42.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | NOEC | 21 | days | 42.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 68.2 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 45.6 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 69 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | growth rate | NOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 68.7 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Reproduction/Progeny counts/numbers | NOEC | 21 | days | 156.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | NOEC | 21 | days | 9.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia cornuta | Reproduction/Progeny counts/numbers | NOEC | 33 | days | 0.00000483 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 45.9 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Palaemonetes pugio | Reproduction/Progeny counts/numbers | LOEL | 21 | days | 26 | μg/L | 16 ECOTOX | Manyin,T., and C.L. Rowe | Reproductive and Life Stage-Specific Effects of Aqueous Copper on the Grass Shrimp, Palaemonetes pugio | Mar. Environ. Res.69(3): 152-157 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Growth (Weight) | NOEL | 21 | days | 130 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 51.9 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 51.1 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 46.5 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia cornuta | Slowed, Retarded, Delayed or Non-development | NOEC | 33 | days | 0.00000483 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | NOEC | 21 | days | 42.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | growth rate | NOEC | 21 | days | 42.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | NOEC | 21 | days | 156.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | NOEC | 21 | days | 156.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Reproduction/Time to first progeny | NOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC10 | 21 | days | 58.2 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | growth rate | NOEC | 21 | days | 21.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Growth rate | NOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia cornuta | Lifespan | NOEC | 33 | days | 0.00000483 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | LOEC | 21 | days | 229.9 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia cornuta | Reproduction/Number of days between eggs laid or litters | NOEC | 33 | days | 0.00000483 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia cornuta | Reproduction/Progeny counts/numbers | NOEC | 33 | days | 0.00000483 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia cornuta | Reproduction/Progeny counts/numbers | NOEC | 33 | days | 0.00000483 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Ceriodaphnia cornuta | Hatch | NOEC | 33 | days | 0.00000483 | g/d/org | 0 g/d/org / 0 g/d/org / 0.00000320 g/d/org / 0.00000483 g/d/org | 16 ECOTOX | Gusso-Choueri,P.K., R.B. Choueri, A.T. Lombardi, and M.G.G. Melao | Effects of Dietary Copper on Life-History Traits of a Tropical Freshwater Cladoceran | Arch. Environ. Contam. Toxicol.62(4): 589-598 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Reproduction/Time to first progeny | NOEC | 21 | days | 42.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | NOEC | 21 | days | 42.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Reproduction/Time to first progeny | NOEC | 21 | days | 42.3 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | NOEC | 21 | days | 85.2 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | LOEC | 14 | days | 30 | μg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | LOEC | 21 | days | 90 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Growth (Dry weight) | LOEC | 21 | days | 90 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 25 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Reproduction/Progeny counts/numbers | LOEC | 16 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Reproduction/Progeny counts/numbers | LOEC | 14 | days | 6.25 | μg/L | 0.88 ug/L / 6.25 ug/L | 16 ECOTOX | Asselman,J., J.R. Shaw, S.P. Glaholt, J.K. Colbourne, and K.A.C. De Schamphelaere | Transcription Patterns of Genes Encoding Four Metallothionein Homologs in Daphnia pulex Exposed to Copper and Cadmium are Time- and Homolog-Dependent | Aquat. Toxicol.142/143:422-430 | 2013 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | NOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Growth rate | EC50 | 21 | days | 102 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | LOEC | 14 | days | 0.03 | mg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | LOEC | 40 | days | 5 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 121 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 48 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | LOEL | 21 | days | 24～48 | μg | 16 ECOTOX | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Reproduction/Progeny counts/numbers | LOEL | 7 | days | 15.9 | μg/g | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Intrinsic rate of increase | LOEL | 15 | days | 90 | μg/L | 16 ECOTOX | Atienzar,F.A., V.V. Cheung, A.N. Jha, and M.H. Depledge | Fitness Parameters and DNA Effects are Sensitive Indicators of Copper-Induced Toxicity in Daphnia magna | Toxicol. Sci.59(2): 241-250 | 2001 | 2022/01/25 | ||||||
| 甲殻類 | Palaemonetes pugio | Reproduction/Progeny counts/numbers | LOEL | days | 26 | μg/L | 16 ECOTOX | Manyin,T., and C.L. Rowe | Reproductive and Life Stage-Specific Effects of Aqueous Copper on the Grass Shrimp, Palaemonetes pugio | Mar. Environ. Res.69(3): 152-157 | 2009 | 2022/01/25 | |||||||
| 甲殻類 | Palaemonetes pugio | Reproduction/Progeny counts/numbers | LOEL | 25 | days | 26 | μg/L | 16 ECOTOX | Manyin,T., and C.L. Rowe | Reproductive and Life Stage-Specific Effects of Aqueous Copper on the Grass Shrimp, Palaemonetes pugio | Mar. Environ. Res.69(3): 152-157 | 2009 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Growth (Weight) | LOEL | 21 | days | 24～48 | μg | 16 ECOTOX | De Schamphelaere,K.A.C., I. Forrez, K. Dierckens, P. Sorgeloos, and C.R. Janssen | Chronic Toxicity of Dietary Copper to Daphnia magna | Aquat. Toxicol.81(4): 409-418 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 5 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | LOEC | 14 | days | 130 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Growth rate | LOEC | 21 | days | 156.5 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 50 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | LOEC | 14 | days | 90 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Net Reproductive Rate | LOEC | 21 | days | 75 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Acclimation of Daphnia magna to Environmentally Realistic Copper Concentrations | Comp. Biochem. Physiol. C Comp. Pharmacol. Toxicol.136(3): 253-264 | 2003 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Growth rate | EC50 | 21 | days | 90 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 70.7 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 56.4 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 21 | days | 69 | μg/L | 16 ECOTOX | Van Leeuwen,C.J., J.L. Buchner, and H. Van Dijk | Intermittent Flow System for Population Toxicity Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol.40(4): 496-502 | 1988 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 97 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 76.3 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 72.7 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 70.5 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 68.5 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | growth rate | EC50 | 21 | days | 79 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 65.2 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Growth rate | EC50 | 21 | days | 356 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Mortality | EC50 | 21 | days | 269 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | Net Reproductive Rate | EC50 | 21 | days | 216 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 67.6 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | LOEC | 21 | days | 90 | μg/L | 16 ECOTOX | Muyssen,B.T.A., and C.R. Janssen | Age and Exposure Duration as a Factor Influencing Cu and Zn Toxicity Toward Daphnia magna | Ecotoxicol. Environ. Saf.68(3): 436-442 | 2007 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Growth rate | EC50 | 21 | days | 160 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia longispina | growth rate | EC50 | 21 | days | 90 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 67.8 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 70.2 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., and C.R. Janssen | Influence of Multigeneration Acclimation to Copper on Tolerance, Energy Reserves, and Homeostasis of Daphnia magna Straus | Environ. Toxicol. Chem.23(8): 2029-2037 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 75.7 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | growth rate | EC50 | 21 | days | 227 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 113 | μg/L | 16 ECOTOX | De Schamphelaere,K.A.C., and C.R. Janssen | Effects of Chronic Dietary Copper Exposure on Growth and Reproduction of Daphnia magna | Environ. Toxicol. Chem.23(8): 2038-2047 | 2004 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | Survival | LC50 | 7 | days | 70.5 | μg/g | 16 ECOTOX | Sofyan,A., J.R. Shaw, and W.J. Birge | Metal Trophic Transfer from Algae to Cladocerans and the Relative Importance of Dietary Metal Exposure | Environ. Toxicol. Chem.25(4): 1034-1041 | 2006 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 79.6 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia longispina | Mortality | EC50 | 21 | days | 98 | μg/L | 0.2 ug/L / 5.5 ug/L / 9.2 ug/L / 21.3 ug/L / 42.3 ug/L / 85.2 ug/L / 156.5 ug/L / 229.9 ug/L | 16 ECOTOX | Agra,A.R., A.M.V.M. Soares, and C. Barata | Life-History Consequences of Adaptation to Pollution. "Daphnia longispina Clones Historically Exposed to Copper" | Ecotoxicology20(3): 552-562 | 2011 | 2022/01/25 | |||||
| 甲殻類 | Daphnia pulex | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 5.11 | μg/L | 0 ug/L / 5-160 ug/L | 16 ECOTOX | Asselman,J., S.P. Glaholt, Z. Smith, G. Smagghe, C.R. Janssen, J.K. Colbourne, J.R. Shaw, and K.A.C. De Schamphelaere | Functional Characterization of Four Metallothionein Genes in Daphnia pulex Exposed to Environmental Stressors | Aquat. Toxicol.110/111:54-65 | 2012 | 2022/01/25 | |||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 21 | days | 44 | μg/L | 16 ECOTOX | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia pulex | Mortality | LC50 | 21 | days | 0.003～3 | μg/L | 16 ECOTOX | Roux,D.J., P.L. Kempster, E. Truter, and L. Van der Merwe | Effect of Cadmium and Copper on Survival and Reproduction of Daphnia pulex | Water SA19(4): 269-274 | 1993 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 74.8 | μg/L | 16 ECOTOX | Bossuyt,B.T.A., Y.R. Escobar, and C.R. Janssen | Multigeneration Acclimation of Daphnia magna Straus to Different Bioavailable Copper Concentrations | Ecotoxicol. Environ. Saf.61(3): 327-336 | 2005 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus purpuratus | Reproduction | EC50 | 1.3 | hours | 25 | μg/L | 16 ECOTOX | Dinnel,P.A., J.M. Link, Q.J. Stober, M.W. Letourneau, and W.E. Roberts | Comparative Sensitivity of Sea Urchin Sperm Bioassays to Metals and Pesticides | Arch. Environ. Contam. Toxicol.18(5): 748-755 | 1989 | 2022/01/25 | ||||||
| 甲殻類 | Dendraster excentricus | Reproduction | EC50 | 1.3 | hours | 26 | μg/L | 16 ECOTOX | Dinnel,P.A., J.M. Link, Q.J. Stober, M.W. Letourneau, and W.E. Roberts | Comparative Sensitivity of Sea Urchin Sperm Bioassays to Metals and Pesticides | Arch. Environ. Contam. Toxicol.18(5): 748-755 | 1989 | 2022/01/25 | ||||||
| 甲殻類 | Dendraster excentricus | Fertilization | EC50 | 60 | minutes | 46.1 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea virginica | Growth (Weight) | LOEL | 30 | days | 0.05 | μg/L | 16 ECOTOX | Krishnamurthy,S. | Effects of Physiochemical Differences and Concentration on Assimilation and Depuration of Copper and Silver in Crassostrea virginica | Ph.D.Thesis, University of Maryland, Eastern Shore, MD:98 p. | 1994 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus droebachiensis | Reproduction | EC50 | 1.3 | hours | 59 | μg/L | 16 ECOTOX | Dinnel,P.A., J.M. Link, Q.J. Stober, M.W. Letourneau, and W.E. Roberts | Comparative Sensitivity of Sea Urchin Sperm Bioassays to Metals and Pesticides | Arch. Environ. Contam. Toxicol.18(5): 748-755 | 1989 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus purpuratus | Fertilization | EC50 | 60 | minutes | 24.7 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus droebachiensis | Fertilization | EC50 | 60 | minutes | 27.5 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Dendraster excentricus | Fertilization | EC50 | 60 | minutes | 24.3 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Fertilization | EC50 | 60 | minutes | 0.026 | mg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Chironomus dilutus | cell number | NOEC | 21 | days | 58.83 | μg/L | 7.03 ug/L / 58.83 ug/L | 16 ECOTOX | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2022/01/25 | |||||
| 甲殻類 | Dendraster excentricus | Fertilization | EC50 | 60 | minutes | 18.4 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Fertilization | EC50 | 60 | minutes | 12.1 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus droebachiensis | Fertilization | EC50 | 60 | minutes | 58.7 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Dendraster excentricus | Fertilization | EC50 | 60 | minutes | 28.3 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Crassostrea gigas | Fertilization | EC50 | 60 | minutes | 0.052 | mg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Strongylocentrotus purpuratus | Fertilization | EC50 | 60 | minutes | 9.3 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | growth | NOEC | 21 | days | 12.6 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 24.1 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 6.3 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | ||||||
| 甲殻類 | Mercenaria mercenaria (hard clam) | development | NOEC | 288 | hours | 7 | μg/L | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | NOEC | 21 | days | 36.8 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 56.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Heijerick DG, Janssen CR | Comparison of the effect of different pH buffering techniques on the toxicity of copper and zinc to Daphnia magna and Pseudokirchneriella subcapitata | Ecotoxicology 13:697-705 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | population growth | NOEC | 21 | days | 36.8 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | aquatic crustacea: Tisbe battagliai | mortality | NOEC | 21 | days | 18 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 28 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 21.5 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 71.4 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 68.8 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 106 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 181 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | aquatic crustacea: Tisbe battagliai | reproduction | NOEC | 21 | days | 18 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | study report | 2021/10/25 | ||||||||
| 甲殻類 | aquatic crustacea: Tisbe battagliai | development | NOEC | 21 | days | 18 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 19 | μg/L | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 10 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | aquatic crustacea: Tisbe battagliai | development | NOEC | 21 | days | 18 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | Waiwood, K.G. & Beamish, F.W.H. | Effects of copper, pH and hardness the critical swimming performance of rainbow trout (Salmo gairdneri Richardson) | Journal of Fish Biology 12, 611-619 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 5.9 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Regenmortel T, Janssen CR, De Schamphelaere KAC | Comparison of the capacity of two biotic ligand models to predict chronic copper toxicity to two Daphnia magna clones and formulation of a generalized bioavailability model | Environmental Toxicology and Chemistry 34(7): 1597-1608 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 8.2 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Regenmortel T, Janssen CR, De Schamphelaere KAC | Comparison of the capacity of two biotic ligand models to predict chronic copper toxicity to two Daphnia magna clones and formulation of a generalized bioavailability model | Environmental Toxicology and Chemistry 34(7): 1597-1608 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 10.3 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 7.9 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 11.5 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Mercenaria mercenaria (hard clam) | development | NOEC | 288 | hours | 7 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | aquatic worm: Neanthes arenaceodentata (polychaete) | growth | NOEC | 28 | days | 12.1 | μg/L [meas. (arithm. mean)] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | ||||||
| 甲殻類 | aquatic worm: Neanthes arenaceodentata (polychaete) | growth | NOEC | 28 | days | 13.5 | μg/L [meas. (arithm. mean)] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | LOEC | 21 | days | 30 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) 225-235 | 2021/10/25 | |||||
| 甲殻類 | aquatic crustacea: Tisbe battagliai | mortality | NOEC | 21 | days | 18 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 10 | μg/L | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 5.7 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 31.6 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 122 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.A. and Janssen, C.R. | Development and field validation of a biotic ligand model predicting chronic copper toxicity to Daphnia magna | Environ Toxicol Chem. 2004;23(6):1365-75 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 20 | μg/L | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.A.C. & Janssen, C.R. | Effects of chronic dietary copper exposure on growth and reproduction of Daphnia magna | Environ Toxicol Chem., 23(8): 2038-2047 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 106 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 75.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 68.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Regenmortel T, Janssen CR, De Schamphelaere KAC | Comparison of the capacity of two biotic ligand models to predict chronic copper toxicity to two Daphnia magna clones and formulation of a generalized bioavailability model | Environmental Toxicology and Chemistry 34(7): 1597-1608 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 118 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 71.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 34.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 10 | μg/L | 12 ECHA Information on Registered Substances | 2 | Bossuyt B.T. and Janssen C.R. | Influence of multi-generation acclimation to copper on tolerance, energy reserves and homeostasis of Daphnia magna | Environmental Toxicol Chem., 23(8), 2029-2037 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 181 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Regenmortel T, Janssen CR, De Schamphelaere KAC | Comparison of the capacity of two biotic ligand models to predict chronic copper toxicity to two Daphnia magna clones and formulation of a generalized bioavailability model | Environmental Toxicology and Chemistry 34(7): 1597-1608 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 20 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 4 | μg/L | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) 225-235 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 57.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 133 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Regenmortel T, Janssen CR, De Schamphelaere KAC | Comparison of the capacity of two biotic ligand models to predict chronic copper toxicity to two Daphnia magna clones and formulation of a generalized bioavailability model | Environmental Toxicology and Chemistry 34(7): 1597-1608 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 28 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 73.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 83.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | EC10 | 7 | days | 46 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC10 | 7 | days | 65 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | EC10 | 7 | days | 29 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Jop, K.M. et al. | Development of a Water-Effect Ratio for Copper, Cadmium and Lead for the Great Works River in Maine Using Ceriodaphnia dubia and Salvelinus fontinalis | Bull. Environ. Contam. Toxicol. 54, 29-35 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | EC10 | 7 | days | 25 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 56.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 50.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | aquatic crustacea: Tisbe battagliai | reproduction | NOEC | 21 | days | 18 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | publication | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 70.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 20 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 15 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 10 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 40 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 5 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 30 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 4 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 4 | μg/L | 12 ECHA Information on Registered Substances | 2 | Adam N, Vakurov A, Knapen D, Blust R | The chronic toxicity of CuO nanoparticles and copper salt to Daphnia magna | Journal of Hazardous materials 283:416-422 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 265 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Regenmortel T, Janssen CR, De Schamphelaere KAC | Comparison of the capacity of two biotic ligand models to predict chronic copper toxicity to two Daphnia magna clones and formulation of a generalized bioavailability model | Environmental Toxicology and Chemistry 34(7): 1597-1608 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 29 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 32.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 46.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 41.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC20 | 21 | days | 12 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC20 | 21 | days | 79.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 17 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 6 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC20 | 21 | days | 19 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 22 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC20 | 21 | days | 36.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC20 | 21 | days | 62.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC20 | 21 | days | 9.5 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 14.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | aquatic mollusc: Mytilus edulis | Embryo development | NOEC | 48 | hours | 6.2 | μg/L [meas. (arithm. mean) Total dissolved + labile Cu] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 21.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 26.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 20 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Heijerick DG, Janssen CR | Comparison of the effect of different pH buffering techniques on the toxicity of copper and zinc to Daphnia magna and Pseudokirchneriella subcapitata | Ecotoxicology 13:697-705 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 18 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Chironomus riparius | growth | NOEC | 10 | days | 16.9 | μg/L | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 1.8 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 8.8 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC10 | 7 | days | 10 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | aquatic mollusc: Mytilus edulis | Embryo development | NOEC | 48 | hours | 6.2 | μg/L [meas. (arithm. mean) Total dissolved + labile Cu] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Heijerick DG, Janssen CR | Comparison of the effect of different pH buffering techniques on the toxicity of copper and zinc to Daphnia magna and Pseudokirchneriella subcapitata | Ecotoxicology 13:697-705 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | EC10 | 7 | days | 34 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 55.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC10 | 7 | days | 91 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | ||||||||||||
| 甲殻類 | Daphnia magna | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | ||||||||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC10 | 7 | days | 200 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 32.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 10.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 76.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, Janssen CR | Influence of multigeneration acclimation to copper on tolerance, energy reserves, and homeostasis of Daphnia magna Straus | Environmental Toxicology and Chemistry 23(8):2029-2037 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC20 | 21 | days | 47 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | ||||||||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC10 | 7 | days | 20 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC20 | 21 | days | 7.1 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia pulex | NOEC | ○ | 20 to 100 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Winner RW & Farrell MP | Acute and chronic toxicity of copper to four species of Daphnia | J Fish Res Board Can, 33 | 2022/01/18 | ||||||||||
| 甲殻類 | Ceriodaphnia dubia | Chronic survival values (geometric mean between NOEC and LOEC) | 7 | days | 24.5～34.6 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Oris JT, Winner RW, & Moore MV | A four-day survival and reproduction toxicity test for Ceriodaphnia dubia | Environ Toxicol Chem, 10 | 2022/01/18 | |||||||
| 甲殻類 | Ceriodaphnia dubia | Chronic survival values (geometric mean between NOEC and LOEC) | 4 | days | 34.6 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Oris JT, Winner RW, & Moore MV | A four-day survival and reproduction toxicity test for Ceriodaphnia dubia | Environ Toxicol Chem, 10 | 2022/01/18 | |||||||
| 甲殻類 | Daphnia magna | NOEC | ○ | 20 to 100 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Winner RW & Farrell MP | Acute and chronic toxicity of copper to four species of Daphnia | J Fish Res Board Can, 33 | 2022/01/18 | ||||||||||
| 甲殻類 | Daphnia magna Daphnia pulex | 28 | days | ○ | 10 and 30 μg Cu/litre | 10 EHC (Environmental Health Criteria) | LeBlanc GA | Effects of copper on the competitive interactions of two species of cladocera | Environ Pollut, A37 | 2022/01/18 | |||||||||
| 甲殻類 | Daphnia ambigua | NOEC | ○ | 20 to 100 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Winner RW & Farrell MP | Acute and chronic toxicity of copper to four species of Daphnia | J Fish Res Board Can, 33 | 2022/01/18 | ||||||||||
| 甲殻類 | Ceriodaphnia dubia | mean brood number | EC50 | 348 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Cowgill UM & Milazzo DP | Comparison of the effect of metallic copper and copper nitrate (CU(CNO-3)2.3H2O) on Ceriodaphnia dubia utilizing the three-brood test | Bull Environ Contam Toxicol, 46 | 2022/01/18 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | total progeny | EC50 | 357 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Cowgill UM & Milazzo DP | Comparison of the effect of metallic copper and copper nitrate (CU(CNO-3)2.3H2O) on Ceriodaphnia dubia utilizing the three-brood test | Bull Environ Contam Toxicol, 46 | 2022/01/18 | ||||||||
| 甲殻類 | Daphnia magna | immobilization | EC50 | 21 | days | 1.4 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Dave G | Effects of copper on growth, reproduction, survival and haemoglobin in Daphnia magna | Comp Biochem Physiol, 78C(2) | 2022/01/18 | ||||||
| 甲殻類 | Daphnia pulex | survival | LOEC | 70 | days | 10 | μg/L [Cu] | ○ | 20 μg Cu/litre for 360 min/day | an average water concentration of 5μg Cu/litre | 10 EHC (Environmental Health Criteria) | Ingersoll CG & Winner RW | Daphnia pulex (De Geer) of daily pulse exposures to copper or cadmium | Environ Toxicol Chem, 1 | 2022/01/18 | ||||
| 甲殻類 | Daphnia magna | LC100 | 21 | days | 110 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | van Leeuwen CJ, Büchner JL, & van Dijk H | Intermittent flow system for population toxicity studies demonstrated with Daphnia and copper | Bull Environ Contam Toxicol, 40 | 2022/01/18 | |||||||
| 甲殻類 | Daphnia magna | carapace length | LOEC | 21 | days | 36.8 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | van Leeuwen CJ, Büchner JL, & van Dijk H | Intermittent flow system for population toxicity studies demonstrated with Daphnia and copper | Bull Environ Contam Toxicol, 40 | 2022/01/18 | ||||||
| 甲殻類 | Daphnia pulex | survival | NOEC | 70 | days | 5 | μg/L [Cu] | ○ | 20 μg Cu/litre for 360 min/day | an average water concentration of 5μg Cu/litre | 10 EHC (Environmental Health Criteria) | Ingersoll CG & Winner RW | Daphnia pulex (De Geer) of daily pulse exposures to copper or cadmium | Environ Toxicol Chem, 1 | 2022/01/18 | ||||
| 甲殻類 | Daphnia parvula | NOEC | ○ | 20 to 100 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Winner RW & Farrell MP | Acute and chronic toxicity of copper to four species of Daphnia | J Fish Res Board Can, 33 | 2022/01/18 | ||||||||||
| 甲殻類 | Daphnia magna | reproductive impairment | EC50 | 3 | weeks | 35 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Biesinger KE & Christensen GM | Effects of various metals on survival, growth, reproduction, and metabolism of Daphnia magna | J Fish Res Board Can, 29 | 2022/01/18 | ||||||
| 甲殻類 | Daphnia magna | LC50 | 3 | weeks | 44 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Biesinger KE & Christensen GM | Effects of various metals on survival, growth, reproduction, and metabolism of Daphnia magna | J Fish Res Board Can, 29 | 2022/01/18 | |||||||
| 甲殻類 | Mytilus edulis | larval mortality | LC50 | 10 | days | ca.10 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Stromgren T & Nielsen MV | Spawning frequency, growth and mortality of Mytilus edulis larvae, exposed to copper and diesel oil | Aquat Toxicol, 21 | 2022/01/18 | ||||||
| 甲殻類 | Mytilus edulis | adult spawning frequency | EC50 | 30 | days | 2 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Stromgren T & Nielsen MV | Spawning frequency, growth and mortality of Mytilus edulis larvae, exposed to copper and diesel oil | Aquat Toxicol, 21 | 2022/01/18 | ||||||
| 甲殻類 | Mytilus edulis | larvae growth | EC50 | 10 | days | 5～6 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Stromgren T & Nielsen MV | Spawning frequency, growth and mortality of Mytilus edulis larvae, exposed to copper and diesel oil | Aquat Toxicol, 21 | 2022/01/18 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mean total young per female | EC50 | 30.7～30.8 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Oris JT, Winner RW, & Moore MV | A four-day survival and reproduction toxicity test for Ceriodaphnia dubia | Environ Toxicol Chem, 10 | 2022/01/18 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | mean brood size | EC50 | 326 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Cowgill UM & Milazzo DP | Comparison of the effect of metallic copper and copper nitrate (CU(CNO-3)2.3H2O) on Ceriodaphnia dubia utilizing the three-brood test | Bull Environ Contam Toxicol, 46 | 2022/01/18 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | total progeny | EC50 | 305 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Cowgill UM & Milazzo DP | Comparison of the effect of metallic copper and copper nitrate (CU(CNO-3)2.3H2O) on Ceriodaphnia dubia utilizing the three-brood test | Bull Environ Contam Toxicol, 46 | 2022/01/18 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | mean brood number | EC50 | 341 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Cowgill UM & Milazzo DP | Comparison of the effect of metallic copper and copper nitrate (CU(CNO-3)2.3H2O) on Ceriodaphnia dubia utilizing the three-brood test | Bull Environ Contam Toxicol, 46 | 2022/01/18 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | mean brood size | EC50 | 304 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Cowgill UM & Milazzo DP | Comparison of the effect of metallic copper and copper nitrate (CU(CNO-3)2.3H2O) on Ceriodaphnia dubia utilizing the three-brood test | Bull Environ Contam Toxicol, 46 | 2022/01/18 | ||||||||
| 甲殻類 | Daphnia magna | intrinsic rate of natural increase | NOEC | 21 | days | 36.8 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | van Leeuwen CJ, Büchner JL, & van Dijk H | Intermittent flow system for population toxicity studies demonstrated with Daphnia and copper | Bull Environ Contam Toxicol, 40 | 2022/01/18 | ||||||
| 甲殻類 | Chironomus tentans | LC50 | 10 | days | 54 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Phipps GL, Mattson VR, & Ankley GT | Relative sensitivity of three freshwater benthic macroinvertebrates to ten contaminants | Arch Environ Contam Toxicol, 28 | 2022/01/18 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mean total young per female | EC50 | 38.2～40.4 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Oris JT, Winner RW, & Moore MV | A four-day survival and reproduction toxicity test for Ceriodaphnia dubia | Environ Toxicol Chem, 10 | 2022/01/18 | ||||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 25.5 | hours | 250 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >25～30 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 25.5 | hours | 558 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Danio rerio | Mortality | NR-ZERO | 7 | days | 30～50 | μg/L | 16 ECOTOX | Rougier,F., A. Menudier, C. Bosgiraud, and J.A. Nicolas | Copper and Zinc Exposure of Zebrafish, Brachydanio rerio (Hamilton-Buchaman): Effects in Experimental Listeria Infection | Ecotoxicol. Environ. Saf.34(2): 134-140 | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >25～30 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | 10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | 10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Danio rerio | Mortality | NOEC | 7 | days | 0.25 | mg/L | 16 ECOTOX | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >25～30 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >25～30 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Danio rerio | Mortality | NOEC | 7 | days | 0.25 | mg/L | 16 ECOTOX | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Growth (Weight) | IC50 | 56 | days | 54 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Growth (Weight) | IC20 | 56 | days | 21.6 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Growth (Weight) | IC01 | 56 | days | 1.1 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | NR-ZERO | 25 | days | 3 | mg/L | 0 mg/L / 1 mg/L / 2 mg/L / 3 mg/L | 16 ECOTOX | Cengiz,M., M.R. Ozen, and R. Atay | Destruction and Accumulation of Copper and Zinc in Various Organ of the Common Carp, Cyprinus carpio | Int. J. Chem.9(2): 75-84 | 1999 | 2022/01/25 | |||||
| 魚類 | Carassius auratus | Growth (Weight) | NOEC | 70 | days | 90 | μg | 16 ECOTOX | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >25～30 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Growth (Weight) | IC10 | 56 | days | 10.8 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | 10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LOEC | 56 | days | 34.4 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-ZERO | hours | 0.95 | μmol/L | 16 ECOTOX | Zia,S., and D.G. McDonald | Role of the Gills and Gill Chloride Cells in Metal Uptake in the Freshwater-Adapted Rainbow Trout, Oncorhynchus mykiss | Can. J. Fish. Aquat. Sci.51(11): 2482-2492 | 1994 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Growth (Weight) | LOEC | 40 | days | 34.4 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Growth (Weight) | NOEC | 56 | days | 9.21 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Growth (Weight) | NOEC | 40 | days | 21.7 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NOEC | 56 | days | 21.7 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-LETH | hours | 44.2 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-LETH | hours | 29 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Growth (Weight) | LOEC | 56 | days | 15.8 | μg/L | 16 ECOTOX | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >10～15 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | 10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | 20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | 20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >20～25 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 7 | hours | 479 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 19.8 | hours | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 21 | hours | 311 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 11.7 | hours | 370 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 13.8 | hours | 240 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.5 | hours | 1207 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 5.3 | hours | 562 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 20 | hours | 738 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 9 | hours | 444 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 5 | hours | 656 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 14.5 | hours | 320 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LT50 | 3 | hours | 960 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 14 | hours | 1100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 5 | hours | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 18 | hours | 1000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LT50 | 5 | hours | 960 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LT50 | 16 | hours | 960 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 23 | hours | 190 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 4 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 20 | hours | 42 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 12 | hours | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 13 | hours | 1000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 14 | hours | 500 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 13 | hours | 750 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC50 | 5 | hours | 27.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC50 | 5 | hours | 29.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 0.5 | hours | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC50 | 5 | hours | 29.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 9.3 | hours | 384 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 6 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 2 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 1 | hours | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 0.5 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 2 | hours | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 4 | hours | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 6 | hours | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC50 | 5 | hours | 27.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 6.25 | days | 29 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 2.08 | days | 44.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 1 | days | 0.95 | μmol/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zia,S., and D.G. McDonald | Role of the Gills and Gill Chloride Cells in Metal Uptake in the Freshwater-Adapted Rainbow Trout, Oncorhynchus mykiss | Can. J. Fish. Aquat. Sci.51(11): 2482-2492 | 1994 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/23 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 7 | hours | 479 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2 | days | 230 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | 1 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F.A., S.C. Tilton, T.K. Bammler, R.P. Beyer, P.L. Stapleton, N.L. Scholz, and E.P. Gallagher | Transcriptional Impact of Organophosphate and Metal Mixtures on Olfaction: Copper Dominates the Chlorpyrifos-Induced Response in Adult Zebrafish | Aquat. Toxicol.102(3/4): 205-215 | 2011 | 2016/03/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 14 | hours | 1100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 20 | hours | 738 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.21 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.66 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.63 | days | 215 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1 | days | 540 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.77 | days | 186 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | 7 | days | 70～150 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, C. Bosgiraud, and J.A. Nicolas | Copper and Zinc Exposure of Zebrafish, Brachydanio rerio (Hamilton-Buchaman): Effects in Experimental Listeria Infection | Ecotoxicol. Environ. Saf.34(2): 134-140 | 1996 | 2016/03/25 | ||||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 9 | hours | 444 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 3.26 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 5.3 | hours | 562 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 21 | hours | 311 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.44 | days | 122 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.06 | days | 157 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 3.8 | days | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | 1 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F.A., S.C. Tilton, T.K. Bammler, R.P. Beyer, P.L. Stapleton, N.L. Scholz, and E.P. Gallagher | Transcriptional Impact of Organophosphate and Metal Mixtures on Olfaction: Copper Dominates the Chlorpyrifos-Induced Response in Adult Zebrafish | Aquat. Toxicol.102(3/4): 205-215 | 2011 | 2016/03/25 | |||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | NOEC | 7 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.06 | days | 558 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.5 | hours | 1207 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 19.8 | hours | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 23 | hours | 190 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.54 | days | 252 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | 7 | days | 30～50 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, C. Bosgiraud, and J.A. Nicolas | Copper and Zinc Exposure of Zebrafish, Brachydanio rerio (Hamilton-Buchaman): Effects in Experimental Listeria Infection | Ecotoxicol. Environ. Saf.34(2): 134-140 | 1996 | 2016/03/25 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Accumulation | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 7 | days | 10.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.06 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Accumulation | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 6 | hours | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 0.5 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 4 | hours | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | NOEC | 7 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | 14 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2016/03/25 | |||||||
| 魚類 | Danio rerio (Zebrafish) | Physiology | NOEC | 7 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Biochemical | 7 | days | 50～150 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., D. Troutaud, A. Ndoye, and P. Deschaux | Non-specific Immune Response of Zebrafish, Brachydanio rerio (Hamilton-Buchanan) Following Copper and Zinc Exposure | Fish Shellfish Immunol.4:115-127 | 1994 | 2016/03/25 | ||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Physiology | 4 | days | 500 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cairns,J.,Jr., and K.W. Thompson | A Computer Interfaced Toxicity Testing System for Simulating Variable Effluent Loading | In: P.L.Levins, J.C.Harris, and K.D.Drewitz (Eds.), EPA-600/9-81-018, Proc.2nd Symp.: Process Measurements for Environmental Assessment, Arthur D.Little, Inc., Cambridge, MA:183-191 | 1981 | 2016/03/25 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | 11 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dew,W.A., C.M. Wood, and G.G. Pyle | Effects of Continuous Copper Exposure and Calcium on the Olfactory Response of Fathead Minnows | Environ. Sci. Technol.46(16): 9019-9026 | 2012 | 2016/03/25 | |||||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | 1 | days | 6.3～40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., S.C. Tilton, T.K. Bammler, R. Beyer, F. Farin, P.L. Stapleton, and E.P. Gallagher | Transcriptional Biomarkers and Mechanisms of Copper-Induced Olfactory Injury in Zebrafish | Environ. Sci. Technol.42(24): 9404-9411 | 2008 | 2016/03/25 | ||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Physiology | 7 | days | 770 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heath,A.G. | Effects of Waterborne Copper or Zinc on the Osmoregulatory Response of Bluegill to a Hypertonic NaCl Challenge | Comp. Biochem. Physiol. C Comp. Pharmacol.88(2): 307-311 | 1987 | 2016/03/25 | |||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | 5 | hours | 5～65 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||||
| 魚類 | Danio rerio (Zebrafish) | Behavior | 0.33 | hours | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Steele,C.W., D.W. Owens, and A.D. Scarfe | Attraction of Zebrafish, Brachydanio rerio, to Alanine and Its Suppression by Copper | J. Fish Biol.36(3): 341-352 | 1990 | 2016/03/25 | |||||||
| 魚類 | Danio rerio (Zebrafish) | Behavior | 0.33 | hours | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Steele,C.W., D.W. Owens, and A.D. Scarfe | Attraction of Zebrafish, Brachydanio rerio, to Alanine and Its Suppression by Copper | J. Fish Biol.36(3): 341-352 | 1990 | 2016/03/25 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Physiology | 500～3000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cairns,J.,Jr., K.W. Thompson, and A.C. Hendricks | Effects of Fluctuating, Sublethal Applications of Heavy Metal Solutions upon the Gill Ventilation Response of Bluegills (Lepomis macrochirus) | EPA-600/3-81-003, U.S.EPA, Cincinnati, OH:104 p. | 1981 | 2016/03/25 | ||||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Accumulation | 2.3～98.9 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nakagawa,H., and S. Ishio | Aspects of Accumulation of Copper, Manganese and Zinc Ions in the Egg of Medaka Oryzias latipes | Nippon Suisan Gakkaishi55(1): 117-121 | 1989 | 2016/03/25 | ||||||||||
| 魚類 | Danio rerio (Zebrafish) | Accumulation | 7 | days | 30～150 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, C. Bosgiraud, and J.A. Nicolas | Copper and Zinc Exposure of Zebrafish, Brachydanio rerio (Hamilton-Buchaman): Effects in Experimental Listeria Infection | Ecotoxicol. Environ. Saf.34(2): 134-140 | 1996 | 2016/03/25 | ||||||||
| 魚類 | Danio rerio (Zebrafish) | Physiology | NOEC | 7 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 4 | days | 15.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 4 | days | 9.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 4 | days | 4.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 7 | days | 4.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 7 | days | 11.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 4 | days | 14.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 7 | days | 3.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 4 | days | 7.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 4 | days | 4.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 7 | days | 11.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 19.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 84.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC20 | 5 | hours | 21.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Cellular Effects | 1 | hours | 25000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wong,M.H., K.C. Luk, and K.Y. Choi | The Effects of Zinc and Copper Salts on Cyprinus carpio and Ctenopharyngodon idellus | Acta Anat.99(4): 450-454 | 1977 | 2016/03/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.67 | days | 119 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LT50 | 16 | hours | 960 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LT50 | 5 | hours | 960 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LT50 | 3 | hours | 960 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | 25 | days | 3000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cengiz,M., M.R. Ozen, and R. Atay | Destruction and Accumulation of Copper and Zinc in Various Organ of the Common Carp, Cyprinus carpio | Int. J. Chem.9(2): 75-84 | 1999 | 2016/03/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | 1 | hours | 10000～100000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wong,M.H., K.C. Luk, and K.Y. Choi | The Effects of Zinc and Copper Salts on Cyprinus carpio and Ctenopharyngodon idellus | Acta Anat.99(4): 450-454 | 1977 | 2016/03/25 | ||||||||
| 魚類 | Cyprinus carpio (Carp) | Cellular Effects | 1 | hours | 25000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wong,M.H., K.C. Luk, and K.Y. Choi | The Effects of Zinc and Copper Salts on Cyprinus carpio and Ctenopharyngodon idellus | Acta Anat.99(4): 450-454 | 1977 | 2016/03/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Growth | 1000～3000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cengiz,M., M.R. Ozen, and R. Atay | Destruction and Accumulation of Copper and Zinc in Various Organ of the Common Carp, Cyprinus carpio | Int. J. Chem.9(2): 75-84 | 1999 | 2016/03/25 | ||||||||||
| 魚類 | Cyprinus carpio (Carp) | Cellular Effects | 1000～3000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cengiz,M., M.R. Ozen, and R. Atay | Destruction and Accumulation of Copper and Zinc in Various Organ of the Common Carp, Cyprinus carpio | Int. J. Chem.9(2): 75-84 | 1999 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 7 | days | 11.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Physiology | 1000～3000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cengiz,M., M.R. Ozen, and R. Atay | Destruction and Accumulation of Copper and Zinc in Various Organ of the Common Carp, Cyprinus carpio | Int. J. Chem.9(2): 75-84 | 1999 | 2016/03/25 | ||||||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 5 | hours | 656 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | EC50 | 85 | days | 46 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | ER01 | 56 | days | 4600 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | ER10 | 56 | days | 6700 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | ER20 | 56 | days | 9000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | ER50 | 56 | days | 15900 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | IC01 | 56 | days | 1.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | IC10 | 56 | days | 10.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | IC20 | 56 | days | 21.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | IC50 | 56 | days | 54 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC20 | 4 | days | 2.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | 1000～3000 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cengiz,M., M.R. Ozen, and R. Atay | Destruction and Accumulation of Copper and Zinc in Various Organ of the Common Carp, Cyprinus carpio | Int. J. Chem.9(2): 75-84 | 1999 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC50 | 5 | hours | 29.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 13.8 | hours | 240 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 9.3 | hours | 384 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2 | days | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 4 | days | 110 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.26 | days | 110 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2 | days | 170 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 3.25 | days | 118 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1 | days | 240 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 4 | days | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 11.7 | hours | 370 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 4 | days | 230 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 747 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 502 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 1200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Eisei Kagaku32(1): 46-53 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 837 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC20 | 5 | hours | 20.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC20 | 5 | hours | 19.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC20 | 5 | hours | 21.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 83.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC50 | 5 | hours | 27.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC50 | 5 | hours | 29.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | EC50 | 5 | hours | 27.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | IC20 | 1 | hours | <2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dew,W.A., C.M. Wood, and G.G. Pyle | Effects of Continuous Copper Exposure and Calcium on the Olfactory Response of Fathead Minnows | Environ. Sci. Technol.46(16): 9019-9026 | 2012 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | IC20 | 4 | days | 6.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dew,W.A., C.M. Wood, and G.G. Pyle | Effects of Continuous Copper Exposure and Calcium on the Olfactory Response of Fathead Minnows | Environ. Sci. Technol.46(16): 9019-9026 | 2012 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 14.5 | hours | 320 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 503 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 530 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 1100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Eisei Kagaku32(1): 46-53 | 1986 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 400 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 647 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 1 | days | 1400 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Eisei Kagaku32(1): 46-53 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 490 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Eisei Kagaku32(1): 46-53 | 1986 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 442 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 1000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cairns,J.,Jr., K.W. Thompson, and A.C. Hendricks | Effects of Fluctuating, Sublethal Applications of Heavy Metal Solutions upon the Gill Ventilation Response of Bluegills (Lepomis macrochirus) | EPA-600/3-81-003, U.S.EPA, Cincinnati, OH:104 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.58 | days | 110 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.95 | days | 110 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.23 | days | 386 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2016/03/25 | ||||||
| 魚類 | Poecilia reticulata (Guppy) | Mortality | LC50 | 4 | days | 66.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,P.D., and L.J. Weber | Toxic Response as a Quantitative Function of Body Size | Toxicol. Appl. Pharmacol.33(3): 471-483 | 1975 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 2 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 2.21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 4 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Physiology | LOEC | 14 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1 | days | 6.44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wang,L., T.K. Bammler, R.P. Beyer, and E.P. Gallagher | Copper-Induced Deregulation of MicroRNA Expression in the Zebrafish Olfactory System | Environ. Sci. Technol.47(13): 7466-7474 | 2013 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1 | days | 6.44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wang,L., T.K. Bammler, R.P. Beyer, and E.P. Gallagher | Copper-Induced Deregulation of MicroRNA Expression in the Zebrafish Olfactory System | Environ. Sci. Technol.47(13): 7466-7474 | 2013 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 6 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1 | days | 6.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., S.C. Tilton, T.K. Bammler, R. Beyer, F. Farin, P.L. Stapleton, and E.P. Gallagher | Transcriptional Biomarkers and Mechanisms of Copper-Induced Olfactory Injury in Zebrafish | Environ. Sci. Technol.42(24): 9404-9411 | 2008 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction | LOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 3.21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 0.5 | hours | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 1 | days | 1800 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Eisei Kagaku32(1): 46-53 | 1986 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 5 | hours | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 636 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Accumulation | LOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 1 | hours | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | NOEC | 2 | hours | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Accumulation | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1 | hours | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 1390 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 900 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,K.W., A.C. Hendricks, and J.,Jr. Cairns | Acute Toxicity of Zinc and Copper Singly and in Combination to the Bluegill (Lepomis macrochirus) | Bull. Environ. Contam. Toxicol.25(1): 122-129 | 1980 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 1100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,K.W., A.C. Hendricks, and J.,Jr. Cairns | Acute Toxicity of Zinc and Copper Singly and in Combination to the Bluegill (Lepomis macrochirus) | Bull. Environ. Contam. Toxicol.25(1): 122-129 | 1980 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 197 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 2200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 1870 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 1250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Academy of Natural Sciences | The Sensitivity of Aquatic Life to Certain Chemicals Commonly Found in Industrial Wastes | Final Rep.No.RG-3965(C2R1), U.S.Public Health Service Grant, Acad.of Nat.Sci., Philadelphia, PA:89 p. | 1960 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 684 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 769 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1.21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 262 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 1 | days | 540 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Eisei Kagaku32(1): 46-53 | 1986 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 473 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 17.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 906 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 2 | days | 890 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Trama,F.B. | The Acute Toxicity of Copper to the Common Bluegill (Lepomis macrochirus Rafinesque) | Not. Nat. Acad. Nat. Sci. Philadelphia 257:1-13 | 1954 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 710 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Trama,F.B. | The Acute Toxicity of Copper to the Common Bluegill (Lepomis macrochirus Rafinesque) | Not. Nat. Acad. Nat. Sci. Philadelphia 257:1-13 | 1954 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 544 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 315 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 300 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 434 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 84 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 1300 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 1.46 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | NOEC | 40 | days | 21.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | LOEC | 56 | days | 9210 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | LOEC | 20 | days | 9.21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LOEC | 56 | days | 34.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | LOEC | 40 | days | 9210 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | LOEC | 56 | days | 15.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 7 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LETC | 14 | days | 14 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 13 | hours | 750 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 13 | hours | 1000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 2.38 | days | 200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 14 | hours | 500 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 2.33 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Biochemical | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Grosell,M.H., C. Hogstrand, and C.M. Wood | Renal Cu and Na Excretion and Hepatic Cu Metabolism in both Cu Acclimated and non Acclimated Rainbow Trout (Oncorhynchus mykiss) | Aquat. Toxicol.40(2/3): 275-291 | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 18 | hours | 1000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 16.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 514 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 10.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 13.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | LOEC | 40 | days | 34.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 43.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | NOEC | 56 | days | 9.21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 31.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 32.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 14.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 39.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 21.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anadu,D.I., G.A. Chapman, L.R. Curtis, and R.A. Tubb | Effect of Zinc Exposure on Subsequent Acute Tolerance to Heavy Metals in Rainbow Trout | Bull. Environ. Contam. Toxicol.43(3): 329-336 | 1989 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 63 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Physiology | 4 | days | 27 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,B.G., T.F. Andrews, D.C. Chandler, and W.J. Jahoda | The Evaluation of Aquatic Invertebrates as Assay Organisms for the Determination of the Toxicity of Industrial Wastes | Final Report 51, American Petroleum Institute Project, Ohio State University, Columbus, OH: | 1948 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 45 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 22 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 38 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 63 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 31 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 70 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 31 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 45 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 10.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knittel,M.D. | Susceptibility of Steelhead Trout Salmo gairdneri Richardson to Redmouth Infection Yersinia ruckeri Following Exposure to Copper | J. Fish Dis.4(1): 33-40 | 1981 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Behavior | 6.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Giattina,J.D., R.R. Garton, and D.G. Stevens | Avoidance of Copper and Nickel by Rainbow Trout as Monitored by a Computer-Based Data Acquisition System | Trans. Am. Fish. Soc.111(4): 491-504 | 1982 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Cellular Effects | 27.8～315 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J.D. Rose, R.A. Jenkins, K.G. Gerow, and H.L. Bergman | Chinook Salmon (Oncorhynchus tshawytscha) and Rainbow Trout (Oncorhynchus mykiss) Exposed to Copper: Neurophysiological and Histological Effects on the Olfactory System | Environ. Toxicol. Chem.18(9): 1979-1991 | 1999 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Biochemical | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Grosell,M.H., C. Hogstrand, and C.M. Wood | Renal Cu and Na Excretion and Hepatic Cu Metabolism in both Cu Acclimated and non Acclimated Rainbow Trout (Oncorhynchus mykiss) | Aquat. Toxicol.40(2/3): 275-291 | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 49 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 2.08 | days | 42.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEC | 56 | days | 21.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 7 | days | 24.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 20 | hours | 42 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 70 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 2.08 | days | 42.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 70 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 44.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 85.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 190 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 3.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Baker,R.J., M.D. Knittel, and J.L. Fryer | Susceptibility of Chinook Salmon, Oncorhynchus tshawytscha (Walbaum), and Rainbow Trout, Salmo gairdneri Richardson, to Infection with Vibrio anguillarum Following Sublethal Copper Exposure | J. Fish Dis.6(3): 267-275 | 1983 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 19.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Baker,R.J., M.D. Knittel, and J.L. Fryer | Susceptibility of Chinook Salmon, Oncorhynchus tshawytscha (Walbaum), and Rainbow Trout, Salmo gairdneri Richardson, to Infection with Vibrio anguillarum Following Sublethal Copper Exposure | J. Fish Dis.6(3): 267-275 | 1983 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 51 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 0.95 | μmol/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zia,S., and D.G. McDonald | Role of the Gills and Gill Chloride Cells in Metal Uptake in the Freshwater-Adapted Rainbow Trout, Oncorhynchus mykiss | Can. J. Fish. Aquat. Sci.51(11): 2482-2492 | 1994 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 78 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 29 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., and D.G. Stevens | Acutely Lethal Levels of Cadmium, Copper, and Zinc to Adult Male Coho Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 837-840 | 1978 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 12 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 5.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 3.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 66 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 4.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 480 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 13.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 2.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 128 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 83.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 197 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 221 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 274 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 2.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 165 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 103 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 243 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 169 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Physiology | 1 | hours | 27.8～315 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J.D. Rose, R.A. Jenkins, K.G. Gerow, and H.L. Bergman | Chinook Salmon (Oncorhynchus tshawytscha) and Rainbow Trout (Oncorhynchus mykiss) Exposed to Copper: Neurophysiological and Histological Effects on the Olfactory System | Environ. Toxicol. Chem.18(9): 1979-1991 | 1999 | 2016/03/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 40.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 23 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 10.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 32.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 56 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Biochemical | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Grosell,M.H., C. Hogstrand, and C.M. Wood | Renal Cu and Na Excretion and Hepatic Cu Metabolism in both Cu Acclimated and non Acclimated Rainbow Trout (Oncorhynchus mykiss) | Aquat. Toxicol.40(2/3): 275-291 | 1998 | 2016/03/25 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 14 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | 50 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | |||||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Behavior | 1.67 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Timms,A.M., H. Kleerekoper, and J. Matis | Locomotor Response of Goldfish, Channel Catfish, and Largemouth Bass to a 'Copper-Polluted' Mass of Water in an Open Field | Water Resour. Res.8(6): 1574-1580 | 1972 | 2016/03/25 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Behavior | 1 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kleerekoper,H., J.B. Waxman, and J. Matis | Interaction of Temperature and Copper Ions as Orienting Stimuli in the Locomotor Behavior of the Goldfish (Carassius auratus) | J. Fish. Res. Board Can.30(6): 725-728 | 1973 | 2016/03/25 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Behavior | 1 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kleerekoper,H., J.B. Waxman, and J. Matis | Interaction of Temperature and Copper Ions as Orienting Stimuli in the Locomotor Behavior of the Goldfish (Carassius auratus) | J. Fish. Res. Board Can.30(6): 725-728 | 1973 | 2016/03/25 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Accumulation | 50 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 101 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Accumulation | 50 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | |||||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | 70 | days | 18～90 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||||
| 魚類 | Carassius auratus (Goldfish) | Cellular Effects | 70 | days | 18～90 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||||
| 魚類 | Carassius auratus (Goldfish) | Accumulation | 1600 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | |||||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | 56 | days | 18～90 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||||
| 魚類 | Carassius auratus (Goldfish) | Behavior | 8 | hours | 11～17 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kleerekoper,H., G.F. Westlake, J.H. Matis, and P.J. Gensler | Orientation of Goldfish (Carassius auratus) in Response to a Shallow Gradient of a Sublethal Concentration of Copper in an Open Field; An Analysis of the Orientation of Goldfish (Carassius auratus) in Response to a Shall | J. Fish. Res. Board Can.29(1): 45-54 | 1971 | 2016/03/25 | ||||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | 42 | days | 18～90 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 9.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 38 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 56 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 31 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 85 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 70 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 45 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 56 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 91 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 31 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 0.0001～0.01 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bilinski,E., and R.E.E. Jonas | Effects of Cadmium and Copper on the Oxidation of Lactate by Rainbow Trout (Salmo gairdneri) Gills | J. Fish. Res. Board Can.30(10): 1553-1558 | 1973 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 85 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 49 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 22 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 49 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 49 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 49 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 31 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 0.95 | μmol/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zia,S., and D.G. McDonald | Role of the Gills and Gill Chloride Cells in Metal Uptake in the Freshwater-Adapted Rainbow Trout, Oncorhynchus mykiss | Can. J. Fish. Aquat. Sci.51(11): 2482-2492 | 1994 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Behavior | 7.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Giattina,J.D., R.R. Garton, and D.G. Stevens | Avoidance of Copper and Nickel by Rainbow Trout as Monitored by a Computer-Based Data Acquisition System | Trans. Am. Fish. Soc.111(4): 491-504 | 1982 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Grosell,M.H., C. Hogstrand, and C.M. Wood | Renal Cu and Na Excretion and Hepatic Cu Metabolism in both Cu Acclimated and non Acclimated Rainbow Trout (Oncorhynchus mykiss) | Aquat. Toxicol.40(2/3): 275-291 | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Behavior | 0～360 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J.C.A. Marr, J. Lipton, D. Cacela, and H.L. Bergman | Differences in Neurobehavioral Responses of Chinook Salmon (Oncorhynchus tshawytscha) and Rainbow Trout (Oncorhynchus mykiss) Exposed to Copper and Cobalt: Behavioral Avoidance | Environ. Toxicol. Chem.18(9): 1972-1978 | 1999 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Biochemical | 20.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Grosell,M.H., C. Hogstrand, and C.M. Wood | Cu Uptake and Turnover in both Cu-Acclimated and Non-acclimated Rainbow Trout (Oncorhynchus mykiss) | Aquat. Toxicol.38:257-276 | 1997 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 20.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Grosell,M.H., C. Hogstrand, and C.M. Wood | Cu Uptake and Turnover in both Cu-Acclimated and Non-acclimated Rainbow Trout (Oncorhynchus mykiss) | Aquat. Toxicol.38:257-276 | 1997 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | 20 | days | 9.21～52.5 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2016/03/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 85 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 11 | days | 57～121 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | <0.9～9 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, H.L. Bergman, J.S. Meyer, and C. Hogstrand | Relationship Between Copper Exposure Duration, Tissue Copper Concentration, and Rainbow Trout Growth | Aquat. Toxicol.36(1-2): 17-30 | 1996 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Biochemical | <0.9～9 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, H.L. Bergman, J.S. Meyer, and C. Hogstrand | Relationship Between Copper Exposure Duration, Tissue Copper Concentration, and Rainbow Trout Growth | Aquat. Toxicol.36(1-2): 17-30 | 1996 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 2 | days | 0.000001 | その他others [M] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bilinski,E., and R.E.E. Jonas | Effects of Cadmium and Copper on the Oxidation of Lactate by Rainbow Trout (Salmo gairdneri) Gills | J. Fish. Res. Board Can.30(10): 1553-1558 | 1973 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Biochemical | 0.0001～0.01 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bilinski,E., and R.E.E. Jonas | Effects of Cadmium and Copper on the Oxidation of Lactate by Rainbow Trout (Salmo gairdneri) Gills | J. Fish. Res. Board Can.30(10): 1553-1558 | 1973 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 4.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, H.L. Bergman, J.S. Meyer, and C. Hogstrand | Relationship Between Copper Exposure Duration, Tissue Copper Concentration, and Rainbow Trout Growth | Aquat. Toxicol.36(1-2): 17-30 | 1996 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 2.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, H.L. Bergman, J.S. Meyer, and C. Hogstrand | Relationship Between Copper Exposure Duration, Tissue Copper Concentration, and Rainbow Trout Growth | Aquat. Toxicol.36(1-2): 17-30 | 1996 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 1 | days | 24.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Grosell,M.H., C. Hogstrand, and C.M. Wood | Cu Uptake and Turnover in both Cu-Acclimated and Non-acclimated Rainbow Trout (Oncorhynchus mykiss) | Aquat. Toxicol.38:257-276 | 1997 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 56 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 56 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 22 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 38 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 85 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 22 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 38 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 45 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 49 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 56 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 45 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 38 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 63 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 78 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 70 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 56 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 42 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 78 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 78 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 78 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 70 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 11 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 85 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 31 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 56 | days | 31 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 38 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 63 | days | 16 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 22 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 22 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 63 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 45 | days | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 63 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 9.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 13.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 3.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 16.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 5.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 28 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 13.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 3.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 16.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 8.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 12.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 9.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 29 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | 17 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 30.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 54 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | 26 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | 21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 11.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | 35.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 308 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 76.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4.5 | days | >34.9～<35.9 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4.5 | days | >81.7～<93 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Growth | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 286 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 297 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 380 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >54.4～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >80～<100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 54.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >60～<80 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >35.9～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 4.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 93 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >93～<100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 35.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >35.9～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 34.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >100～<120 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 81.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >140～<160 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 53.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >35.9～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >60～<80 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 35.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4.5 | days | >53.6～<54.4 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 21.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 16.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 53.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 36.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 19 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 12 | hours | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 80 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 37.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 21.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 52.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 17.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 35.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 67.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 27.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 7.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 46.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2016/03/25 | |||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 16.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Accumulation | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Accumulation | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Accumulation | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1 | days | 6.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., S.C. Tilton, T.K. Bammler, R. Beyer, F. Farin, P.L. Stapleton, and E.P. Gallagher | Transcriptional Biomarkers and Mechanisms of Copper-Induced Olfactory Injury in Zebrafish | Environ. Sci. Technol.42(24): 9404-9411 | 2008 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction | LOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Accumulation | LOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1 | days | 6.44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wang,L., T.K. Bammler, R.P. Beyer, and E.P. Gallagher | Copper-Induced Deregulation of MicroRNA Expression in the Zebrafish Olfactory System | Environ. Sci. Technol.47(13): 7466-7474 | 2013 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1.21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | 7 | days | 30～50 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, C. Bosgiraud, and J.A. Nicolas | Copper and Zinc Exposure of Zebrafish, Brachydanio rerio (Hamilton-Buchaman): Effects in Experimental Listeria Infection | Ecotoxicol. Environ. Saf.34(2): 134-140 | 1996 | 2017/03/15 | ||||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 1 | days | 6.44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wang,L., T.K. Bammler, R.P. Beyer, and E.P. Gallagher | Copper-Induced Deregulation of MicroRNA Expression in the Zebrafish Olfactory System | Environ. Sci. Technol.47(13): 7466-7474 | 2013 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 32.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 27.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 5.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.06 | days | 157 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 19 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 35.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 169 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 80 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 10.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 43.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 40.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 10.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 32.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 36.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.26 | days | 110 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Physiology | NOEC | 7 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | NOEC | 7 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 3.21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | NOEC | 7 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.23 | days | 386 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 4 | days | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 4 | days | 230 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.21 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 3.8 | days | 220 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 58.83 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.95 | days | 110 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 3.26 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.54 | days | 252 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.06 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | 25 | days | 3000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cengiz,M., M.R. Ozen, and R. Atay | Destruction and Accumulation of Copper and Zinc in Various Organ of the Common Carp, Cyprinus carpio | Int. J. Chem.9(2): 75-84 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | EC50 | 85 | days | 46 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | IC10 | 56 | days | 10.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | IC50 | 56 | days | 54 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 21.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2 | days | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 2 | days | 890 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Trama,F.B. | The Acute Toxicity of Copper to the Common Bluegill (Lepomis macrochirus Rafinesque) | Not. Nat. Acad. Nat. Sci. Philadelphia 257:1-13 | 1954 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 165 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 4.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 12 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 1300 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 636 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1 | days | 540 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 300 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 442 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 1 | days | 1400 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 84 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 197 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 4 | days | 110 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | 14 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 37.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1 | days | 240 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 3.25 | days | 118 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.66 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.44 | days | 122 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.77 | days | 186 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 13.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.58 | days | 110 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2 | days | 230 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2 | days | 170 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 2.67 | days | 119 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.06 | days | 558 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 1 | days | 1800 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2017/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | LC50 | 1.63 | days | 215 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 400 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 544 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 1870 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 2200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 262 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 1390 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 710 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Trama,F.B. | The Acute Toxicity of Copper to the Common Bluegill (Lepomis macrochirus Rafinesque) | Not. Nat. Acad. Nat. Sci. Philadelphia 257:1-13 | 1954 | 2017/03/15 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 1200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2017/03/15 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 1000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cairns,J.,Jr., K.W. Thompson, and A.C. Hendricks | Effects of Fluctuating, Sublethal Applications of Heavy Metal Solutions upon the Gill Ventilation Response of Bluegills (Lepomis macrochirus) | EPA-600/3-81-003, U.S.EPA, Cincinnati, OH:104 p. | 1981 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 473 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 315 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 17.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 747 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Physiology | LOEC | 14 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2017/03/15 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 1250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Academy of Natural Sciences | The Sensitivity of Aquatic Life to Certain Chemicals Commonly Found in Industrial Wastes | Final Rep.No.RG-3965(C2R1), U.S.Public Health Service Grant, Acad.of Nat.Sci., Philadelphia, PA:89 p. | 1960 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 906 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Poecilia reticulata (Guppy) | Mortality | LC50 | 4 | days | 66.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,P.D., and L.J. Weber | Toxic Response as a Quantitative Function of Body Size | Toxicol. Appl. Pharmacol.33(3): 471-483 | 1975 | 2017/03/15 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 900 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,K.W., A.C. Hendricks, and J.,Jr. Cairns | Acute Toxicity of Zinc and Copper Singly and in Combination to the Bluegill (Lepomis macrochirus) | Bull. Environ. Contam. Toxicol.25(1): 122-129 | 1980 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 434 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 530 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 769 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 684 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 1 | days | 540 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 837 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 1100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Thompson,K.W., A.C. Hendricks, and J.,Jr. Cairns | Acute Toxicity of Zinc and Copper Singly and in Combination to the Bluegill (Lepomis macrochirus) | Bull. Environ. Contam. Toxicol.25(1): 122-129 | 1980 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Physiology | LC50 | 4 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 503 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 502 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 490 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2017/03/15 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 1100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Cellular Effects | LOEC | 2.21 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Linbo,T.L., C.M. Stehr, J.P. Incardona, and N.L. Scholz | Dissolved Copper Triggers Cell Death in the Peripheral Mechanosensory System of Larval Fish | Environ. Toxicol. Chem.25(2): 597-603 | 2006 | 2017/03/15 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 647 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >100～<120 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >93～<100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4.5 | days | >81.7～<93 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 93 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >140～<160 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >25～<30 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 53.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 84.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 101 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 83.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 34.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 13.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >35.9～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 35.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 81.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4.5 | days | >34.9～<35.9 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | 35.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >35.9～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 35.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 76.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >35.9～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 67.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | 17 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 514 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 9.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 4.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | LOEC | 56 | days | 15.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 5.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 5.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 16.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 31.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 56 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 46.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Physiology | NOEC | 7 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Growth | NOEC | 70 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 56 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 2.38 | days | 200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 2.08 | days | 42.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 7 | days | 24.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | NOEC | 56 | days | 9.21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEC | 56 | days | 21.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | NOEC | 40 | days | 21.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Physiology | 4 | days | 27 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,B.G., T.F. Andrews, D.C. Chandler, and W.J. Jahoda | The Evaluation of Aquatic Invertebrates as Assay Organisms for the Determination of the Toxicity of Industrial Wastes | Final Report 51, American Petroleum Institute Project, Ohio State University, Columbus, OH: | 1948 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 190 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 1.46 | days | 250 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 3.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Baker,R.J., M.D. Knittel, and J.L. Fryer | Susceptibility of Chinook Salmon, Oncorhynchus tshawytscha (Walbaum), and Rainbow Trout, Salmo gairdneri Richardson, to Infection with Vibrio anguillarum Following Sublethal Copper Exposure | J. Fish Dis.6(3): 267-275 | 1983 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 7 | days | 50 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LOEC | 56 | days | 34.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | LOEC | 56 | days | 9210 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | LOEC | 40 | days | 34.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | LOEC | 20 | days | 9.21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | LOEC | 40 | days | 9210 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, P.G. Welsh, J. Morris, D. Cacela, and M.J. Suedkamp | Relationship Between Exposure Duration, Tissue Residues, Growth, and Mortality in Rainbow Trout (Oncorhynchus mykiss) Juveniles Sub-chronically Exposed to Copper | Aquat. Toxicol.58(3/4): 175-188 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 2.08 | days | 42.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LT50 | 2.33 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 42 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 14 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 14 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 70 | days | 121 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2017/03/15 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 274 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 42 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 36 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 19.25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Baker,R.J., M.D. Knittel, and J.L. Fryer | Susceptibility of Chinook Salmon, Oncorhynchus tshawytscha (Walbaum), and Rainbow Trout, Salmo gairdneri Richardson, to Infection with Vibrio anguillarum Following Sublethal Copper Exposure | J. Fish Dis.6(3): 267-275 | 1983 | 2017/03/15 | |||||||
| 魚類 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 90 | その他others [ug] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Life,J.S. | Metabolism and Pharmacodynamics of Copper (Cu++) in the Goldfish (Carassius auratus) | Ph.D.Thesis, University of Michigan, MI:117 p. | 1970 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 8.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 12.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 380 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 128 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 3.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 39.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 66 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 21.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 28 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 13.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | 26 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 243 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 221 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 3.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 13.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 57 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A., and D.G. Stevens | Acutely Lethal Levels of Cadmium, Copper, and Zinc to Adult Male Coho Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 837-840 | 1978 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 3.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 19.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 16.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 9.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 15 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 11.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 30.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >40～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 35 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 17.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >10～<15 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 9.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 1.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 52.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 21.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | 25 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >5～<10 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 120 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 29 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anadu,D.I., G.A. Chapman, L.R. Curtis, and R.A. Tubb | Effect of Zinc Exposure on Subsequent Acute Tolerance to Heavy Metals in Rainbow Trout | Bull. Environ. Contam. Toxicol.43(3): 329-336 | 1989 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 16.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 2.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 2.8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 7.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 14.5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 83.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | 20 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 15.9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 6 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | 4 | days | 51 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | >20～<25 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4.5 | days | >53.6～<54.4 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 17.2 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 7 | days | 4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 8.33 | days | 21 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >15～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | >80～<100 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >60～<80 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 54 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 53.6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 297 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 480 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 54.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 18 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1.5 | days | >60～<80 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | >0～<20 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 197 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 308 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 5 | days | 286 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2.5 | days | >20～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test Re | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 103 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 23 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3 | days | 60 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 3.5 | days | >54.4～<60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2017/03/15 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 85.3 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2017/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GROWTHB | EC50 | 85 | days | 0.046 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GROWTHB | EC50 | 78 | days | 0.027 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GROWTHB | LOEL | 78 | days | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | NOEC | 45 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | NOEC | 49 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | NOEC | 56 | days | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | NOEC | 63 | days | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | NOEC | 70 | days | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | LOEL | 78 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Nebeker ea 86 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GROWTHB | LOEL | 45 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | LOEL | 22 | days | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GROWTHB | NOEC | 63 | days | 0.016 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | LOEL | 70 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | NOEC | 78 | days | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Nebeker ea 86 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL, GROWTHB | LOEL | 31 | days | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GROWTHB | NOEC | 45 | days | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GROWTHB | LOEL | 63 | days | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GROWTHB | NOEC | 78 | days | 0.016 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | LOEL | 63 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | LOEL | 56 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | LOEL | 49 | days | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | LOEL | 45 | days | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL, GROWTHB | NOEC | 31 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | LOEL | 38 | days | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | NOEC | 38 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | NOEC | 22 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss | mortality | LOEC | 1080 | hours | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | NOEC | 1176 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | NOEC | 1080 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | NOEC | 912 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | LOEC | 744 | hours | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | NOEC | 744 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | LOEC | 744 | hours | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | LOEC | 1872 | hours | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | EC50 | 1872 | hours | 0.027 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | EC50 | 2040 | hours | 0.046 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | LOEC | 1344 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | NOEC | 744 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | LOEC | 528 | hours | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | NOEC | 528 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | LOEC | 1080 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | NOEC | 1080 | hours | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | NOEC | 1872 | hours | 0.016 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | LOEC | 1512 | hours | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | NOEC | 1344 | hours | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | NOEC | 1512 | hours | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | LOEC | 1512 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | LOEC | 1872 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | NOEC | 1680 | hours | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | LOEC | 1680 | hours | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | growth | NOEC | 1512 | hours | 0.016 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | LOEC | 1176 | hours | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | LOEC | 912 | hours | 0.121 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | NOEC | 1872 | hours | 0.031 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >5～10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 24 | hours | 20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 83.6 | μg/L | <0.16 ug/L / <0.16 ug/L / 38.0 ug/L / 38.3 ug/L / 71.8 ug/L / 71.8 ug/L / 141 ug/L / 146 ug/L / 289 ug/L / 290 ug/L / 608 ug/L / 592 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 16.1 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | 40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 35 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 101 | μg/L | <0.16 ug/L / <0.16 ug/L / 38.0 ug/L / 38.3 ug/L / 71.8 ug/L / 71.8 ug/L / 141 ug/L / 146 ug/L / 289 ug/L / 290 ug/L / 608 ug/L / 592 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 32.8 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >60～80 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >5～10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 34.9 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 36.7 | μg/L | 16 ECOTOX | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 35.9 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 9.9 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >15～20 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 54 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 15.2 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 15.6 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 48 | hours | 503 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >15～20 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 24 | hours | >80～100 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 12 | hours | 120 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >60～80 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >20～25 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 35.1 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 169 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 43.4 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 12 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 3.4 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | 40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | 60 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 21.2 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 54.4 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 14.5 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 53.6 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 16.6 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 120 | μg/L | 3.3 ug/L / 25 ug/L / 51 ug/L / 97 ug/L / 170 ug/L / 350 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 108 | hours | >53.6～54.4 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | 15 | μg/L | 16 ECOTOX | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 66 | μg/L | 16 ECOTOX | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 80 | μg/L | 16 ECOTOX | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 200 | hours | 15 | μg/L | 16 ECOTOX | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | 40 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 30.7 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 84.3 | μg/L | <0.16 ug/L / <0.16 ug/L / 38.0 ug/L / 38.3 ug/L / 71.8 ug/L / 71.8 ug/L / 141 ug/L / 146 ug/L / 289 ug/L / 290 ug/L / 608 ug/L / 592 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 4 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 11.9 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 3.4 | μg/L | 0 ug/L / 3.2 ug/L / 5.6 ug/L / 10 ug/L / 18 ug/L / 32 ug/L / 56 ug/L / 100 ug/L | 16 ECOTOX | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >10～15 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 19 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 15.9 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 9.2 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >20～25 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 8 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 60 | hours | >35.9～40 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 12.7 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >35.9～40 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 83.3 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 9.1 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >25～30 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 13.3 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 60 | hours | 60 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | 15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 13.2 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 128 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 46.2 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 24 | hours | 60 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 10.4 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 60 | hours | >20～40 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >10～15 | μg/L | <0.9 ug/L / 5.76 ug/L / 11.23 ug/L / 20.82 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | 20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 24 | hours | >40～60 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 24 | hours | >40～60 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | 30 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >20～25 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 10 | μg/L | <0.9 ug/L / 5.17 ug/L / 10.27 ug/L / 20.01 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | 35.9 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 180 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 37 | hours | 252 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Danio rerio | Mortality | NR-LETH | 14 | days | 0.25 | mg/L | 16 ECOTOX | Rougier,F., A. Menudier, D. Troutaud, C. Bosgiraud, A. Ndoye, J.A. Nicolas, and P. Deschaux | In Vivo Effect of Zinc and Copper on the Development of Listeriosis in Zebrafish, Brachydanio rerio (Hamilton-Buchanan) | J. Fish Dis.15(5): 453-456 | 1992 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 684 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 250 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Lepomis macrochirus | Survival | LC50 | 96 | hours | 1250 | μg/L | 16 ECOTOX | Academy of Natural Sciences | The Sensitivity of Aquatic Life to Certain Chemicals Commonly Found in Industrial Wastes | Final Rep.No.RG-3965(C2R1), U.S.Public Health Service Grant, Acad.of Nat.Sci., Philadelphia, PA:89 p. | 1960 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 906 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Oryzias latipes | Mortality | LC50 | 24 | hours | 540 | μg/L | 16 ECOTOX | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2022/01/25 | ||||||
| 魚類 | Lepomis macrochirus | Mortality | LC50 | 48 | hours | 890 | μg/L | 16 ECOTOX | Trama,F.B. | The Acute Toxicity of Copper to the Common Bluegill (Lepomis macrochirus Rafinesque) | Not. Nat. Acad. Nat. Sci. Philadelphia 257:1-13 | 1954 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 48 | hours | 120 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cymatogaster aggregata | Mortality | LC50 | 96 | hours | 417.7 | μg/L | 16 ECOTOX | Dinnel,P.A., Q.J. Stober, J.M. Link, M.W. Letourneau, W.E. Roberts, S.P. Felton, and R.E. Nakatani | Methodology and Validation of a Sperm Cell Toxicity Test for Testing Toxic Substances in Marine Waters | Final Rep.FRI-UW-8306, Fish.Res.Inst., Schl.of Fish., Univ.of Washington, Seattle, WA:208 p. | 1983 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 48 | hours | 400 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Poecilia reticulata | Mortality | LC50 | 96 | hours | 0.139 | mg/L | 16 ECOTOX | Anderson,P.D., and L.J. Weber | Toxic Response as a Quantitative Function of Body Size | Toxicol. Appl. Pharmacol.33(3): 471-483 | 1975 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 262 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 473 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Oryzias latipes | Mortality | LC50 | 48 | hours | 490 | μg/L | 16 ECOTOX | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 24 | hours | 180 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 96 | hours | 530 | μg/L | 5.7 ug/L / 84 ug/L / 160 ug/L / 310 ug/L / 620 ug/L / 1200 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 魚類 | Dicentrarchus labrax | Mortality | LC50 | 48 | hours | 2500 | ng/g | 16 ECOTOX | Romeo,M., N. Bennani, M. Gnassia-Barelli, M. LaFaurie, and J.P. Girard | Cadmium and Copper Display Different Responses Towards Oxidative Stress in the Kidney of the Sea Bass Dicentrarchus labrax | Aquat. Toxicol.48(2/3): 185-194 | 2000 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 14 | hours | 1100 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 7 | hours | 479 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 29.5 | hours | 386 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 14.5 | hours | 320 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 78.3 | hours | 250 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 48 | hours | 837 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 39 | hours | 215 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 24 | hours | 240 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Lepomis macrochirus | Mortality | LC50 | 96 | hours | 710 | μg/L | 16 ECOTOX | Trama,F.B. | The Acute Toxicity of Copper to the Common Bluegill (Lepomis macrochirus Rafinesque) | Not. Nat. Acad. Nat. Sci. Philadelphia 257:1-13 | 1954 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 19.8 | hours | 220 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Lagodon rhomboides | Mortality | LC50 | 72 | hours | 4140 | μg/L | 16 ECOTOX | Steele,C.W. | Comparison of the Behavioural and Acute Toxicity of Copper to Sheepshead, Atlantic Croaker and Pinfish | Mar. Pollut. Bull.14(11): 425-428 | 1983 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 64 | hours | 119 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 54.3 | hours | 110 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 96 | hours | 110 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 9 | hours | 444 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 49.5 | hours | 157 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Lagodon rhomboides | Mortality | LC50 | 48 | hours | 4430 | μg/L | 16 ECOTOX | Steele,C.W. | Comparison of the Behavioural and Acute Toxicity of Copper to Sheepshead, Atlantic Croaker and Pinfish | Mar. Pollut. Bull.14(11): 425-428 | 1983 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 70.8 | hours | 110 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 8 | days | 90 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 315 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Cymatogaster aggregata | Mortality | LC50 | 96 | hours | 418 | μg/L | 16 ECOTOX | Dinnel,P.A., J.M. Link, Q.J. Stober, M.W. Letourneau, and W.E. Roberts | Comparative Sensitivity of Sea Urchin Sperm Bioassays to Metals and Pesticides | Arch. Environ. Contam. Toxicol.18(5): 748-755 | 1989 | 2022/01/25 | ||||||
| 魚類 | Oryzias latipes | Mortality | LC50 | 48 | hours | 1100 | μg/L | 16 ECOTOX | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2022/01/25 | ||||||
| 魚類 | Oryzias latipes | Mortality | LC50 | 24 | hours | 1800 | μg/L | 16 ECOTOX | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2022/01/25 | ||||||
| 魚類 | Lagodon rhomboides | Mortality | LC50 | 96 | hours | 2750 | μg/L | 16 ECOTOX | Steele,C.W. | Comparison of the Behavioural and Acute Toxicity of Copper to Sheepshead, Atlantic Croaker and Pinfish | Mar. Pollut. Bull.14(11): 425-428 | 1983 | 2022/01/25 | ||||||
| 魚類 | Lagodon rhomboides | Mortality | LC50 | 24 | hours | 7350 | μg/L | 16 ECOTOX | Steele,C.W. | Comparison of the Behavioural and Acute Toxicity of Copper to Sheepshead, Atlantic Croaker and Pinfish | Mar. Pollut. Bull.14(11): 425-428 | 1983 | 2022/01/25 | ||||||
| 魚類 | Lepomis macrochirus | Mortality | LC50 | 96 | hours | 1000 | μg/L | 16 ECOTOX | Cairns,J.,Jr., K.W. Thompson, and A.C. Hendricks | Effects of Fluctuating, Sublethal Applications of Heavy Metal Solutions upon the Gill Ventilation Response of Bluegills (Lepomis macrochirus) | EPA-600/3-81-003, U.S.EPA, Cincinnati, OH:104 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 8 | days | 900 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 197 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 17 | days | 30 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 12 | days | 900 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 12 | days | 300 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 1 | days | 2000 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 91.3 | hours | 220 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 13.8 | hours | 240 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 96 | hours | 120 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 12 | days | 1000 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Citharichthys stigmaeus | Mortality | LC50 | 96 | hours | 800 | μg/L | 16 ECOTOX | Salazar,M.H., and S.M. Salazar | Acute Effects of (bis)Tributyltin Oxide on Marine Organisms | Tech.Rep.No.1299, Naval Ocean Systems Ctr., San Diego, CA:87 p. | 1989 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 544 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Oryzias latipes | Mortality | LC50 | 48 | hours | 1200 | μg/L | 16 ECOTOX | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 96 | hours | 84 | μg/L | 4.2 ug/L / 11 ug/L / 14 ug/L / 27 ug/L / 42 ug/L / 84 ug/L / 170 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 769 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 48 | hours | 647 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 300 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 96 | hours | 442 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 96 | hours | 502 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 96 | hours | 434 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 17.4 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Lepomis macrochirus | Mortality | LC50 | 96 | hours | 1100 | μg/L | 16 ECOTOX | Thompson,K.W., A.C. Hendricks, and J.,Jr. Cairns | Acute Toxicity of Zinc and Copper Singly and in Combination to the Bluegill (Lepomis macrochirus) | Bull. Environ. Contam. Toxicol.25(1): 122-129 | 1980 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 48 | hours | 636 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 1390 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Oryzias latipes | Mortality | LC50 | 24 | hours | 1400 | μg/L | 16 ECOTOX | Tsuji,S., Y. Tonogai, Y. Ito, and S. Kanoh | The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes) | Jpn. J. Toxicol. Environ. Health32(1): 46-53 | 1986 | 2022/01/25 | ||||||
| 魚類 | Lepomis macrochirus | Mortality | LC50 | 96 | hours | 900 | μg/L | 16 ECOTOX | Thompson,K.W., A.C. Hendricks, and J.,Jr. Cairns | Acute Toxicity of Zinc and Copper Singly and in Combination to the Bluegill (Lepomis macrochirus) | Bull. Environ. Contam. Toxicol.25(1): 122-129 | 1980 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Immobilization | LC50 | 96 | hours | 1870 | μg/L | 16 ECOTOX | Van Genderen,E., R. Gensemer, C. Smith, R. Santore, and A. Ryan | Evaluation of the Biotic Ligand Model Relative to Other Site-Specific Criteria Derivation Methods for Copper in Surface Waters with Elevated | Aquat. Toxicol.84(2): 279-291 | 2007 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 9.3 | hours | 384 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Lepomis macrochirus | Mortality | LC50 | 96 | hours | 1300 | μg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LT50 | 16 | hours | 960 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 168 | hours | 10.2 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 37.8 | hours | 110 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 39.8 | hours | 250 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 96 | hours | 2.4 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 96 | hours | 15.7 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 96 | hours | 4.8 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 168 | hours | 4.6 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 42.5 | hours | 186 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Mortality | LC50 | 48 | hours | 747 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 18.1 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 58.5 | hours | 122 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 168 | hours | 11.6 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LT50 | 3 | hours | 960 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 48 | hours | 170 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >35.9～40 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Lepomis macrochirus | Mortality | LC50 | 96 | hours | 2200 | μg/L | 16 ECOTOX | Blaylock,B.G., M.L. Frank, and J.F. McCarthy | Comparative Toxicity of Copper and Acridine to Fish, Daphnia and Algae | Environ. Toxicol. Chem.4(1): 63-71 | 1985 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 168 | hours | 11.4 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 108 | hours | >34.9～35.9 | μg/L | <0.16 ug/L / <0.16 ug/L / 10.6 ug/L / 10.6 ug/L / 21.2 ug/L / 20.2 ug/L / 38.8 ug/L / 39.2 ug/L / 85.8 ug/L / 84.8 ug/L / 163 ug/L / 166 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 5.1 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 96 | hours | 9.7 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 168 | hours | 3.9 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 96 | hours | 7.3 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 168 | hours | 11.9 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LT50 | 5 | hours | 960 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | >54.4～60 | μg/L | <0.16 ug/L / 0.30 ug/L / 10.4 ug/L / 10.6 ug/L / 22.1 ug/L / 20.3 ug/L / 38.5 ug/L / 37.3 ug/L / 85.8 ug/L / 83.7 ug/L / 180 ug/L / 180 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 96 | hours | 14.2 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 1 | days | 3000 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 24 | hours | 540 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 2.5 | hours | 1207 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 96 | hours | 230 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 5 | hours | 656 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 14.6 | days | 900 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 23 | hours | 190 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 8 | days | 30 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 78 | hours | 118 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 5.3 | hours | 562 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 29 | hours | 180 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 11.7 | hours | 370 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 48 | hours | 230 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 20 | hours | 738 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Mortality | LC50 | 21 | hours | 311 | μg/L | 16 ECOTOX | Harrison,F.L.,Jr., and D.W.,Jr. Rice | The Sensitivity of Adult, Embryonic, and Larval Carp Cyprinus carpio to Copper | UCRL-52726, U.S.Nuclear Regulatory Commission, Lawrence Livermore Lab., Livermore, CA:36 p. | 1981 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 1 | days | 3000 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC20 | 96 | hours | 4.7 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 21.7 | μg/L | <0.9 ug/L / 4.59 ug/L / 9.95 ug/L / 20.97 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 16.5 | days | 90 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 15.8 | days | 300 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Clupea harengus | Mortality | ET50 | 8 | days | 300 | μg/L | 16 ECOTOX | Blaxter,J.H.S. | The Effect of Copper on the Eggs and Larvae of Plaice and Herring | J. Mar. Biol. Assoc. U.K.57:849-858 | 1977 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LETHAL | EC50 | 4 | days | 0.08 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 17 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 16.3 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 29 | μg/L | 16 ECOTOX | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 0.48 | mg/L | 16 ECOTOX | Tisler,T., and J. Zagorc-Koncan | Aquatic Toxicity of Selected Chemicals as a Basic Criterion for Environmental Classification | Arh. Hig. Rada Toksikol.54(3): 207-213 | 2003 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 85.3 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 8.1 | μg/L | 0 ug/L / 3.2 ug/L / 5.6 ug/L / 10 ug/L / 18 ug/L / 32 ug/L / 56 ug/L / 100 ug/L | 16 ECOTOX | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 2.8 | μg/L | 16 ECOTOX | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >20～40 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 28 | μg/L | 16 ECOTOX | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 60 | hours | >20～40 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >20～40 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 165 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 15.1 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 10.1 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | 20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 32 | μg/L | 0 ug/L / 10 ug/L / 20 ug/L / 40 ug/L / 80 ug/L / 160 ug/L / 320 ug/L | 16 ECOTOX | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 27.7 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | 20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 76.6 | μg/L | 0.22 ug/L / 0.28 ug/L / 31.4 ug/L / 30.9 ug/L / 46.8 ug/L / 47.1 ug/L / 75.1 ug/L / 75.2 ug/L / 119 ug/L / 122 ug/L / 195 ug/L / 191 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 31.9 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | 25 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Cyprinus carpio | mortality | LC50 | 96 | hours | 810 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2), p 225-235 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 24 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 37.3 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 5.7 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 7 | μg/L | 16 ECOTOX | Anadu,D.I., G.A. Chapman, L.R. Curtis, and R.A. Tubb | Effect of Zinc Exposure on Subsequent Acute Tolerance to Heavy Metals in Rainbow Trout | Bull. Environ. Contam. Toxicol.43(3): 329-336 | 1989 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 39.3 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 15.2 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 13.7 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 17 | μg/L | 16 ECOTOX | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 60 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 21.1 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 18 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 24 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 67.9 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | >20～40 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 60 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | 20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 4.8 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 60 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 514 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 1.8 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 18.1 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 200 | hours | 21 | μg/L | 16 ECOTOX | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 4.2 | μg/L | 16 ECOTOX | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 103 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 17.9 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 17.2 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 221 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 243 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 200 | hours | 26 | μg/L | 16 ECOTOX | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 18 | μg/L | 16 ECOTOX | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 197 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 380 | μg/L | 2.5 ug/L / 52 ug/L / 110 ug/L / 190 ug/L / 380 ug/L / 780 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 3.1 | μg/L | 16 ECOTOX | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 13.1 | μg/L | 16 ECOTOX | Welsh,P.G., J. Lipton, C.A. Mebane, and J.C.A. Marr | Influence of Flow-Through and Renewal Exposures on the Toxicity of Copper to Rainbow Trout | Ecotoxicol. Environ. Saf.69(2): 199-208 | 2008 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 4 | days | 0.11 | mg/L | 16 ECOTOX | Birge,W.J., J.A. Black, A.G. Westerman, and B.A. Ramey | Fish and Amphibian Embryos - a Model System for Evaluating Teratogenicity | Fundam. Appl. Toxicol.3:237-242 | 1983 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >40～60 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 17.2 | μg/L | 0 ug/L / 10 ug/L / 20 ug/L / 40 ug/L / 80 ug/L / 160 ug/L / 320 ug/L | 16 ECOTOX | Welsh,P.G., J. Lipton, G.A. Chapman, and T.L. Podrabsky | Relative Importance of Calcium and Magnesium in Hardness-Based Modification of Copper Toxicity | Environ. Toxicol. Chem.19(6): 1624-1631 | 2000 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 2.3 | μg/L | 16 ECOTOX | Cusimano,R.F., D.F. Brakke, and G.A. Chapman | Effects of pH on the Toxicities of Cadmium, Copper, and Zinc to Steelhead Trout (Salmo gairdneri) | Can. J. Fish. Aquat. Sci.43(8): 1497-1503 | 1986 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >20～40 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | 23 | μg/L | 16 ECOTOX | Marr,J.C.A., J.A. Hansen, J.S. Meyer, D. Cacela, T. Podrabsky, J. Lipton, and H.L. Bergman | Toxicity of Cobalt and Copper to Rainbow Trout: Application of a Mechanistic Model for Predicting Survival | Aquat. Toxicol.43(4): 225-238 | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | 40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 200 | hours | 17 | μg/L | 16 ECOTOX | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >10～15 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 7.9 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | 25 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | >5～10 | μg/L | <0.9 ug/L / 4.90 ug/L / 9.71 ug/L / 18.98 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >140～160 | μg/L | 0.22 ug/L / 0.28 ug/L / 31.4 ug/L / 30.9 ug/L / 46.8 ug/L / 47.1 ug/L / 75.1 ug/L / 75.2 ug/L / 119 ug/L / 122 ug/L / 195 ug/L / 191 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >15～20 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 308 | μg/L | 0.29 ug/L / 0.35 ug/L / 24.5 ug/L / 25.2 ug/L / 63.4 ug/L / 65.1 ug/L / 147 ug/L / 146 ug/L / 300 ug/L / 291 ug/L / 602 ug/L / 601 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-ZERO | 96 | hours | 19.25 | μg/L | 16 ECOTOX | Baker,R.J., M.D. Knittel, and J.L. Fryer | Susceptibility of Chinook Salmon, Oncorhynchus tshawytscha (Walbaum), and Rainbow Trout, Salmo gairdneri Richardson, to Infection with Vibrio anguillarum Following Sublethal Copper Exposure | J. Fish Dis.6(3): 267-275 | 1983 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-ZERO | 96 | hours | 51 | μg/L | 3.3 ug/L / 25 ug/L / 51 ug/L / 97 ug/L / 170 ug/L / 350 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 35.5 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | 20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 286 | μg/L | 0.29 ug/L / 0.35 ug/L / 24.5 ug/L / 25.2 ug/L / 63.4 ug/L / 65.1 ug/L / 147 ug/L / 146 ug/L / 300 ug/L / 291 ug/L / 602 ug/L / 601 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 53.9 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LT50 | 56 | hours | 100 | μg/L | 16 ECOTOX | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 21 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 274 | μg/L | 16 ECOTOX | Chakoumakos,C., R.C. Russo, and R.V. Thurston | Toxicity of Copper to Cutthroat Trout (Salmo clarki) Under Different Conditions of Alkalinity, pH, and Hardness | Environ. Sci. Technol.13(2): 213-219 | 1979 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 60 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >20～25 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 16.1 | μg/L | <0.9 ug/L / 5.73 ug/L / 10.75 ug/L / 20.48 ug/L | 16 ECOTOX | Marr,J.C.A., J. Lipton, D. Cacela, J.A. Hansen, J.S. Meyer, and H.L. Bergman | Bioavailability and Acute Toxicity of Copper to Rainbow Trout (Oncorhynchus mykiss) in the Presence of Organic Acids Simulating Natural Dissolved Organic Carbon | Can. J. Fish. Aquat. Sci.56(8): 1471-1483 | 1999 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 36 | hours | >40～60 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >20～40 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LT50 | 14 | hours | 500 | μg/L | 16 ECOTOX | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-ZERO | 96 | hours | 190 | μg/L | 2.5 ug/L / 52 ug/L / 110 ug/L / 190 ug/L / 380 ug/L / 780 ug/L | 16 ECOTOX | Hammermeister,D., C. Northcott, L. Brooke, and D. Call | Comparison of Copper, Lead and Zinc Toxicity to Four Animal Species in Laboratory and St. Louis River Water | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI:19 p. | 1982 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-ZERO | 96 | hours | 3.9 | μg/L | 16 ECOTOX | Baker,R.J., M.D. Knittel, and J.L. Fryer | Susceptibility of Chinook Salmon, Oncorhynchus tshawytscha (Walbaum), and Rainbow Trout, Salmo gairdneri Richardson, to Infection with Vibrio anguillarum Following Sublethal Copper Exposure | J. Fish Dis.6(3): 267-275 | 1983 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-LETH | 168 | hours | 24.7 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-LETH | 50 | hours | 42.8 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-LETH | 50 | hours | 42.4 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-LETH | 4 | days | 0.75 | mg/L | 16 ECOTOX | Birge,W.J., J.A. Black, A.G. Westerman, and B.A. Ramey | Fish and Amphibian Embryos - a Model System for Evaluating Teratogenicity | Fundam. Appl. Toxicol.3:237-242 | 1983 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 297 | μg/L | 0.29 ug/L / 0.35 ug/L / 24.5 ug/L / 25.2 ug/L / 63.4 ug/L / 65.1 ug/L / 147 ug/L / 146 ug/L / 300 ug/L / 291 ug/L / 602 ug/L / 601 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Immobilization | MATC | 96 | hours | 0.027 | ppm | 16 ECOTOX | Anderson,B.G., T.F. Andrews, D.C. Chandler, and W.J. Jahoda | The Evaluation of Aquatic Invertebrates as Assay Organisms for the Determination of the Toxicity of Industrial Wastes | Final Report 51, American Petroleum Institute Project, Ohio State University, Columbus, OH: | 1948 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 15.9 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LT50 | 13 | hours | 750 | μg/L | 16 ECOTOX | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LT50 | 57 | hours | 200 | μg/L | 16 ECOTOX | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LT50 | 35 | hours | 250 | μg/L | 16 ECOTOX | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LT50 | 18 | hours | 1000 | μg/L | 16 ECOTOX | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LT50 | 168 | hours | 50 | μg/L | 16 ECOTOX | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LT50 | 13 | hours | 1000 | μg/L | 16 ECOTOX | Rombough,P.J. | The Influence of the Zona radiata on the Toxicities of Zinc, Lead, Mercury, Copper and Silver Ions to Embryos of Steelhead Trout Salmo gairdneri | Comp. Biochem. Physiol. C Comp. Pharmacol.82(1): 115-117 | 1985 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-LETH | 20 | hours | 42 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 19.2 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 17.9 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 18 | μg/L | 16 ECOTOX | Chapman,G.A. | Toxicities of Cadmium, Copper, and Zinc to Four Juvenile Stages of Chinook Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 841-847 | 1978 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | 20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 40.1 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 168 | hours | 32.9 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 18 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 144 | hours | >0～20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 52.5 | μg/L | 16 ECOTOX | Naddy,R.B., W.A. Stubblefield, J.R. May, S.A. Tucker, and J.R. Hockett | The Effect of Calcium and Magnesium Ratios on the Toxicity of Copper to Five Aquatic Species in Freshwater | Environ. Toxicol. Chem.21(2): 347-352 | 2002 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | >20～40 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 24 | hours | >40～60 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 57 | μg/L | 16 ECOTOX | Chapman,G.A., and D.G. Stevens | Acutely Lethal Levels of Cadmium, Copper, and Zinc to Adult Male Coho Salmon and Steelhead | Trans. Am. Fish. Soc.107(6): 837-840 | 1978 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 93 | μg/L | 0.22 ug/L / 0.28 ug/L / 31.4 ug/L / 30.9 ug/L / 46.8 ug/L / 47.1 ug/L / 75.1 ug/L / 75.2 ug/L / 119 ug/L / 122 ug/L / 195 ug/L / 191 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | 120 | μg/L | 0.22 ug/L / 0.28 ug/L / 31.4 ug/L / 30.9 ug/L / 46.8 ug/L / 47.1 ug/L / 75.1 ug/L / 75.2 ug/L / 119 ug/L / 122 ug/L / 195 ug/L / 191 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 48 | hours | >0～20 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 108 | hours | >81.7～93 | μg/L | 0.22 ug/L / 0.28 ug/L / 31.4 ug/L / 30.9 ug/L / 46.8 ug/L / 47.1 ug/L / 75.1 ug/L / 75.2 ug/L / 119 ug/L / 122 ug/L / 195 ug/L / 191 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | 20 | μg/L | 16 ECOTOX | Cacela,D., R. Hudson, J. Lipton, J. Marr, T. Podrabsky, and P. Welsh | Preliminary Toxicological Evaulation U.S. v. Iron Mountain Mines, Inc. Vol. 1 Data Report | Report, Prepared for Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of the Attorney General by Hagler Bailly Consulting Inc., Boulder, CO:53 p. | 1996 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 72 | hours | 100 | μg/L | 0.22 ug/L / 0.28 ug/L / 31.4 ug/L / 30.9 ug/L / 46.8 ug/L / 47.1 ug/L / 75.1 ug/L / 75.2 ug/L / 119 ug/L / 122 ug/L / 195 ug/L / 191 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 96 | hours | 5.6 | μg/L | 16 ECOTOX | Welsh,P., J. Lipton, R. Hudson, T. Podrabsky, and D. Cacela | Data Report: Acute Copper Toxicity to Salmonids in Surface Waters in the Vicinity of the Iron Moutain Mine, California. Volume I: Study Objectives, Methods Summary, Water Chemistry Characterization and Toxicity Test R | Report Prepared by Hagler Baily Services, Inc.for: Breidenbach, Buckley, Huchting, Halm & Hamblet, California Office of Attorney General:142 p. | 1998 | 2022/01/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 60 | hours | >100～120 | μg/L | 0.22 ug/L / 0.28 ug/L / 31.4 ug/L / 30.9 ug/L / 46.8 ug/L / 47.1 ug/L / 75.1 ug/L / 75.2 ug/L / 119 ug/L / 122 ug/L / 195 ug/L / 191 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 120 | hours | 81.7 | μg/L | 0.22 ug/L / 0.28 ug/L / 31.4 ug/L / 30.9 ug/L / 46.8 ug/L / 47.1 ug/L / 75.1 ug/L / 75.2 ug/L / 119 ug/L / 122 ug/L / 195 ug/L / 191 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | LC50 | 84 | hours | >93～100 | μg/L | 0.22 ug/L / 0.28 ug/L / 31.4 ug/L / 30.9 ug/L / 46.8 ug/L / 47.1 ug/L / 75.1 ug/L / 75.2 ug/L / 119 ug/L / 122 ug/L / 195 ug/L / 191 ug/L | 16 ECOTOX | Hansen,J.A., J. Lipton, and P.G. Welsh | Relative Sensitivity of Bull Trout (Salvelinus confluentus) and Rainbow Trout (Oncorhynchus mykiss) to Acute Copper Toxicity | Environ. Toxicol. Chem.21(3): 633-639 | 2002 | 2022/01/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 544 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 148.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 197 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1390 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 315 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 17.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 262 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Lepomis macrochirus | mortality | LC50 | 96 | hours | 710 | μg/L [nominal element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 180 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 470 | μg/L [nominal element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1400 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 830 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >830 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 650 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | <=560 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 21.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 820 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Lepomis macrochirus | mortality | LC50 | 96 | hours | 1100 | μg/L [meas. (geom. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Cyprinus carpio | mortality | LC50 | 96 | hours | 800 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 390 | μg/L [nominal test mat.] | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 760 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Dehghani S, Akbari S, Soltanian S, Shamsaei HA, Parvizi S | Comparison of tissue-specific Cu bioaccumulation patterns and sensitivity to waterborne Cu in two freshwater fish: common carp (Cyprinus carpio) and its subspecies mirror carp | World Journal of Fish and Marine Sciences 4(4):349-355 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 580 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Johnson BM, Chao MM, Tedrow OR, McQueen AD, Rodgers JH Jr. | Responses of Lepomis macrochirus, Pimephales promelas, Hyalella azteca, Ceriodaphnia dubia, and Daphnia magna to exposures of Algimycin PWF and copper sulfate pentahydrate | Journal of Aquatic Plant Management 46:176-183 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >12.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 690 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Alsop D, Wood CM | Metal uptake and acute toxicity in zebrafish: common mechanisms across multiple metals | Aquatic Toxicology 105:385-393 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >55.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | NOEC | 96 | hours | 13 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >13 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 920 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Alsop D, Wood CM | Metal uptake and acute toxicity in zebrafish: common mechanisms across multiple metals | Aquatic Toxicology 105:385-393 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | NOEC | 96 | hours | 12.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 680 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 600 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 750 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 960 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 490 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 96 | hours | 13.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >24.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | NOEC | 96 | hours | 29.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 820 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Alsop D, Wood CM | Metal uptake and acute toxicity in zebrafish: common mechanisms across multiple metals | Aquatic Toxicology 105:385-393 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 70.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 26.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 183 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 183 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 182.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 181 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 176.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 175.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 172.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 122.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 112 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 92.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 189.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 75.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 190.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 70.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 58.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 52.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 44.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 36.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 26.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 5.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 18.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 363.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1564 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 468.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 422.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 77 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 20.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 62.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 62.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 42.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Dwyer FJ, Mayer FL, Sappington LC, Buckler DR, Bridges CM, Greer IE, Hardesty DK, Henke CE, Ingersoll CG, Kunz JL, Whites DW, Augspurger T, Mount DR, Hattala K, Neuderfer GN | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part I. Acute toxicity of five chemicals | Archives of Environmental Contamination and Toxicology 48:143-154 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 42.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 35 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 28 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 26.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 684 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 23.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 103 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 20.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 183 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 12.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 460 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 44 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 15 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 271.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 268.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 262.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 253.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 242.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 226.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 223.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 199.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 191.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 190.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 17.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 8.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 85.3 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 94 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 210 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 190 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 200 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 286 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 164 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 2.8 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 4.2 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 93 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 6.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 68 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 9.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 80 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 253 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 149 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 35 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 57 | μg/L [meas. (geom. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 102 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 516 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 309 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 30 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 36.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 59 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 19.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 60.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 42.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 59 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 59.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality + immobility combined | LC50 | 96 | hours | 63 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality + immobility combined | LC50 | 96 | hours | 40.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality + immobility combined | LC50 | 96 | hours | 50.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 19.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | >89 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 42.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 18 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 59.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 56.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 62.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 212.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 11.66 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 148.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 30.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 9.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 5.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 19.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 60.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 596.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Stauber JL, Wilde KL, Markich SJ, Brown PL, Franklin NM, Creighton NM, Janssen CR | Toward a biotic ligand model for freshwater green algae: surface-bound and internal copper are better predictors of toxicity than free Cu2+ ion activity when pH is varied | Environmental Science and Technology 39(7):2067-2072 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1526 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 56.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 62.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality + immobility combined | LC50 | 96 | hours | 60 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 29 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 18 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 17 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 28 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 494.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 82.2 | μg/L [meas. (geom. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1949 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 2034 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 283.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 597.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Grosell, M. et al. | Physiology is pivotal for interactions between salinity and acute copper toxicity to fish and invertebrates | Aquat Toxicol. 2007; 84(2):162-72 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 259.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Erikson, R.J. et al. | The effects of water chemistry on the toxicity of copper to fathead minnows | Environ Toxicol Chem., 15, 181-193. | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 137 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan, A.C. et al. | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model. | Environ Toxicol Chem., 23(6):1567-74 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 21.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 16.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 12.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Bossuyt B.T. and Janssen C.R. | Long-term acclimation of Pseudokirchneriella subcapitata (Korshikov) Hindak to different copper concentrations: changes in tolerance and physiology | Aquatic Toxicology, 68(1): 61-74 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 10.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 300 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 906 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 102 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 41.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 250 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 243 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 24 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 22 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 21 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 40 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 40 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 22.4 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 28.9 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 890 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 429 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 274 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 774.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 83.3 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 31.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 169 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 106.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 96.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 129 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1959 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 613.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 402.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 70 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 128 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 473 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 830 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 750 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 690 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 600 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 38.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 256.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 47.4 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 197 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1870 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 750 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 769 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Cyprinus carpio | mortality | LC50 | 96 | hours | 820 | μg/L [element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 230 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 212.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 11.66 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 19.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 21 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Lepomis macrochirus | mortality | LC50 | 96 | hours | 770 | μg/L [estimated element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 298 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 283.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Adam N, Vakurov A, Knapen D, Blust R | The chronic toxicity of CuO nanoparticles and copper salt to Daphnia magna | Journal of Hazardous materials 283:416-422 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 752.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 698 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 996.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 905.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 892.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 953 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 644.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 521 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 930 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 289.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 820 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 513 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Adam N, Vakurov A, Knapen D, Blust R | The chronic toxicity of CuO nanoparticles and copper salt to Daphnia magna | Journal of Hazardous materials 283:416-422 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 311 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Adam N, Vakurov A, Knapen D, Blust R | The chronic toxicity of CuO nanoparticles and copper salt to Daphnia magna | Journal of Hazardous materials 283:416-422 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 99.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 31.9 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 81.1 | μg/L [meas. (arithm. mean) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 297 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Adam N, Vakurov A, Knapen D, Blust R | The chronic toxicity of CuO nanoparticles and copper salt to Daphnia magna | Journal of Hazardous materials 283:416-422 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 450 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 870 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 646.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 289.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 395.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 229.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Cerda, B and Olive, J.H. | Effects of Diet on Seven-Day Ceriodaphnia dubia Toxicity Tests | Ohio J. Sci. 93 (3): 44-47, 1993 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 230 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >200 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 79.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 71.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 172.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Jop, K.M. et al. | Development of a Water-Effect Ratio for Copper, Cadmium and Lead for the Great Works River in Maine Using Ceriodaphnia dubia and Salvelinus fontinalis | Bull. Environ. Contam. Toxicol. 54, 29-35 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 168.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Jop, K.M. et al. | Development of a Water-Effect Ratio for Copper, Cadmium and Lead for the Great Works River in Maine Using Ceriodaphnia dubia and Salvelinus fontinalis | Bull. Environ. Contam. Toxicol. 54, 29-35 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 167.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Jop, K.M. et al. | Development of a Water-Effect Ratio for Copper, Cadmium and Lead for the Great Works River in Maine Using Ceriodaphnia dubia and Salvelinus fontinalis | Bull. Environ. Contam. Toxicol. 54, 29-35 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 514 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 663 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 150.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1681 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 726.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 383.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 499.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 2013 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1514 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 671.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1405 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 167.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 490 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 653.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 758.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 940.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 210 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 390 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 360 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 770 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Heijerick DG, Janssen CR | Comparison of the effect of different pH buffering techniques on the toxicity of copper and zinc to Daphnia magna and Pseudokirchneriella subcapitata | Ecotoxicology 13:697-705 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 730 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 193 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Cerda, B and Olive, J.H. | Effects of Diet on Seven-Day Ceriodaphnia dubia Toxicity Tests | Ohio J. Sci. 93 (3): 44-47, 1993 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 840 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 151 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1090 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 920 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 337.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 46.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 165 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 221 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 143 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 148.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 630 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 860 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 84 | μg/L [nominal element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 465 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 127.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 113.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 103.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 101.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 84.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 83.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 81.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 980 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 75 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 111.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 650 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 865 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 540 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 645 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1000 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 110.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 114.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 430 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 78.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 94 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 117.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 122.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 123.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 125.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 125.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 126.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 12.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 4.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 96 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 96.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 171 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 496 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 405.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 370.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 292.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Santore, R.C. et al. | Biotic ligand model of the acute toxicity of metals. 2. Application to acute copper toxicity in freshwater fish and Daphnia | Environ Toxicol Chem. 2001; 20(10):2397-402 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | <640 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 68.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 70.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 77.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 97.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 167.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 470 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1060 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >800 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 950 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 660 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 750 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 750 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 149 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 35 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 820 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 172.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 410 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 166.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 160.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 158.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 155.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 152 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 137.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 132.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 131.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 129.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 136.5 | μg/L [nominal element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >780 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 427 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >449 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 363 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 232 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Lepomis macrochirus | mortality | LC50 | 96 | hours | 9150 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Lepomis macrochirus | mortality | LC50 | 96 | hours | 4300 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Lepomis macrochirus | mortality | LC50 | 96 | hours | 4250 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Lepomis macrochirus | mortality | LC50 | 96 | hours | 1000 | μg/L [meas. (geom. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 52 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >810 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >610 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 640 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 780 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >800 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 970 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 810 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 940 | μg/L [meas. (initial) dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 8300 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Geckler JR, Horning WB, Neiheisel TM, Pickering QH, Robinson EL, & Stephan CE | Validity of laboratory tests for predicting copper toxicity in streams | Duluth, Minnesota, US Environmental Protection Agency (EPA-600/3-76-116) | 2022/01/18 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 154 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/01/25 | |||||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 48 | hours | 19000 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Burton DT & Fisher DJ | Acute toxicity of cadmium, copper, zinc, ammonia, 3,3'-dichlorobenzidine, 2,6-dichloro-4-nitroaniline, methylene chloride, and 2,4,6-trichlorophenol to juvenile grass shrimp and killifish | Bull Environ Contam Toxicol, 44 | 2022/03/02 | |||||||
| 魚類 | Cymatogaster aggregata (Shiner perch) | LC50 | 96 | hours | 418 | μg/L | 10 EHC (Environmental Health Criteria) | Dinnell PA, Link JM, Stober QJ, Letourneau MW, & Roberts WE | Comparative sensitivity of sea urchin sperm bioassays to metals and pesticides | Arch Environ Contam Toxicol, 18 | 2022/02/16 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 440 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Geckler JR, Horning WB, Neiheisel TM, Pickering QH, Robinson EL, & Stephan CE | Validity of laboratory tests for predicting copper toxicity in streams | Duluth, Minnesota, US Environmental Protection Agency (EPA-600/3-76-116) | 2022/03/02 | |||||||
| 魚類 | Cyprinus carpio (Carp) | LC50 | 48 | hours | 289 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Peres I & Pihan JC | Copper LC50 to Cyprinus carpio. Influence of hardness, seasonal variation, proposition of maximum acceptable toxicant concentration | Environ Technol, 12 | 2022/01/18 | |||||||
| 魚類 | Oncorhynchus mykiss | mortality | EC50 | 96 | hours | 0.08 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim WK, Curtis LR, Glenn SW, Chapman GA | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously and intermittently exposed to copper | Can J Fish Aquat Sci 41 | 2022/01/24 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 490 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Geckler JR, Horning WB, Neiheisel TM, Pickering QH, Robinson EL, & Stephan CE | Validity of laboratory tests for predicting copper toxicity in streams | Duluth, Minnesota, US Environmental Protection Agency (EPA-600/3-76-116) | 2022/03/02 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 10000 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Geckler JR, Horning WB, Neiheisel TM, Pickering QH, Robinson EL, & Stephan CE | Validity of laboratory tests for predicting copper toxicity in streams | Duluth, Minnesota, US Environmental Protection Agency (EPA-600/3-76-116) | 2022/01/18 | |||||||
| 魚類 | Carassius auratus (Goldfish) | LC50 | 96 | hours | 13800 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/02/08 | |||||||
| 魚類 | Cyprinus carpio (Carp) | LC50 | 48 | hours | 118 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Peres I & Pihan JC | Copper LC50 to Cyprinus carpio. Influence of hardness, seasonal variation, proposition of maximum acceptable toxicant concentration | Environ Technol, 12 | 2022/01/18 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 980 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/01/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | LC50 | 48 | hours | 751 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Peres I & Pihan JC | Copper LC50 to Cyprinus carpio. Influence of hardness, seasonal variation, proposition of maximum acceptable toxicant concentration | Environ Technol, 12 | 2022/01/18 | |||||||
| 魚類 | Cyprinus carpio (Carp) | LC50 | 96 | hours | 300 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Alam MK & Maughan OE | The effect of malathion, diazinon, and various concentrations of zinc, copper, nickel, lead, iron, and mercury on fish | Biol Trace Elem Res, 34(3) | 2022/02/08 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 838 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/02/08 | |||||||
| 魚類 | Cyprinus carpio (Carp) | LC50 | 96 | hours | 1000 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Alam MK & Maughan OE | The effect of malathion, diazinon, and various concentrations of zinc, copper, nickel, lead, iron, and mercury on fish | Biol Trace Elem Res, 34(3) | 2022/02/08 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 490 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Pickering Q, Brungs W, & Gast M | Effect of exposure time and copper concentration on reproduction of the fathead minnow (Pimephales promelas) | Water Res, 11 | 2022/03/02 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 460 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Pickering Q, Brungs W, & Gast M | Effect of exposure time and copper concentration on reproduction of the fathead minnow (Pimephales promelas) | Water Res, 11 | 2022/03/02 | |||||||
| 魚類 | Leiostomus xanthurus (Spot) | LC50 | 96 | hours | 280 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL | Acute toxicity handbook of chemicals to estuarine organisms | Gulf Breeze, Florida, US Environmental Protection Agency, Environmental Research Laboratory (EPA/600/8-87/017) | 2022/01/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | LC50 | 96 | hours | 800 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Rehwoldt R, Menapace LW, Nerrie B, & Alessandrello D | The effect of increased temperature upon the acute toxicity of some heavy metal ions | Bull Environ Contam Toxicol, 8 | 2022/01/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 17 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Chapman GA | Toxicities of cadmium, copper, and zinc to four juvenile stages of chinook salmon and steelhead | Trans Am Fish Soc, 107(6) | 2022/01/18 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 390 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Curtis MW, Copeland TL, & Ward CH | Acute toxicity of 12 industrial chemicals to freshwater and saltwater organisms | Water Res, 13 | 2022/01/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 20.4 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/01/25 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 35.9 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 57 | μg/L | 10 EHC (Environmental Health Criteria) | Chapman GA & Stevens DG | Acutely lethal levels of cadmium, copper, and zinc to adult male coho salmon and steelhead | Trans Am Fish Soc, 107(6) | 2022/01/18 | ||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 3280 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 18 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Chapman GA | Toxicities of cadmium, copper, and zinc to four juvenile stages of chinook salmon and steelhead | Trans Am Fish Soc, 107(6) | 2022/01/18 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 13700 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/01/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 28 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Chapman GA | Toxicities of cadmium, copper, and zinc to four juvenile stages of chinook salmon and steelhead | Trans Am Fish Soc, 107(6) | 2022/01/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 135 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/02/08 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 13.8 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Buhl KJ & Hamilton SJ | Comparative toxicity of inorganic contaminants released by placer mining to early life stages of salmonids | Ecotoxicol Environ Saf, 20 | 2022/02/08 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 7340 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/02/08 | |||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | LC50 | 96 | hours | >220 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Hutchinson TH, Williams TD, & Eales GJ | Toxicity of cadmium, hexavalent chromium and copper to marine fish larvae (Cyprinodon variegatus) and copepods (Tisbe battagliai) | Mar Environ Res, 38 | 2022/01/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 121 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/01/25 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 884 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL & Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 chemicals and 66 species of freshwater animals | Washington, DC, US Department of Interior, Fish and Wildlife Service (Resource Publication 160) | 2022/02/08 | |||||||
| 魚類 | Menidia peninsulae | LC50 | 96 | hours | 140 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Mayer FL | Acute toxicity handbook of chemicals to estuarine organisms | Gulf Breeze, Florida, US Environmental Protection Agency, Environmental Research Laboratory, 274 pp (EPA/600/8-87/017) | 2022/02/16 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 29 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Chapman GA | Toxicities of cadmium, copper, and zinc to four juvenile stages of chinook salmon and steelhead | Trans Am Fish Soc, 107(6) | 2022/01/18 | |||||||
| 魚類 | Pimephales promelas | Growth (Condition index) | NOEC | 21 | days | 58.83 | μg/L | 7.03 ug/L / 58.83 ug/L | 16 ECOTOX | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Growth | EC50 | 85 | days | 46 | μg/L | 16 ECOTOX | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Abnormal development | NOEC | 21 | days | 58.83 | μg/L | 7.03 ug/L / 58.83 ug/L | 16 ECOTOX | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2022/01/25 | |||||
| 魚類 | Pimephales promelas | Survival | NOEC | 21 | days | 58.83 | μg/L | 7.03 ug/L / 58.83 ug/L | 16 ECOTOX | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2022/01/25 | |||||
| 魚類 | Pimephales promelas | Growth (Condition index) | NOEC | 21 | days | 58.83 | μg/L | 7.03 ug/L / 58.83 ug/L | 16 ECOTOX | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2022/01/25 | |||||
| 魚類 | Citharichthys stigmaeus | Mortality | LC50 | 14 | days | 250 | μg/L | 16 ECOTOX | Salazar,M.H., and S.M. Salazar | Acute Effects of (bis)Tributyltin Oxide on Marine Organisms | Tech.Rep.No.1299, Naval Ocean Systems Ctr., San Diego, CA:87 p. | 1989 | 2022/01/25 | ||||||
| 魚類 | Pimephales promelas | Reproduction/Spawning frequency | NOEC | 21 | days | 58.83 | μg/L | 7.03 ug/L / 58.83 ug/L | 16 ECOTOX | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2022/01/25 | |||||
| 魚類 | Pimephales promelas | Reproduction/Progeny counts/numbers | NOEC | 21 | days | 58.83 | μg/L | 7.03 ug/L / 58.83 ug/L | 16 ECOTOX | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2022/01/25 | |||||
| 魚類 | Pimephales promelas | Reproduction/Size | LOEC | 21 | days | 58.83 | μg/L | 7.03 ug/L / 58.83 ug/L | 16 ECOTOX | Ouellette,J.D., M.G. Dube, and S. Niyogi | A Single Metal, Metal Mixture, and Whole-Effluent Approach to Investigate Causes of Metal Mine Effluent Effects on Fathead Minnows (Pimephales promelas) | Water Air Soil Pollut.224(1462): 44 p. | 2013 | 2022/01/25 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality | NR-LETH | 70 | days | 121 | μg/L | 16 ECOTOX | Seim,W.K., L.R. Curtis, S.W. Glenn, and G.A. Chapman | Growth and Survival of Developing Steelhead Trout (Salmo gairdneri) Continuously or Intermittently Exposed to Copper | Can. J. Fish. Aquat. Sci.41(3): 433-438 | 1984 | 2022/01/25 | ||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 47.13 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 15 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 6.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 4.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 4.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 16 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | weight | EC10 | 30 | days | >22 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 7.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | dry weight, biomass | NOEC | 28 | days | 13 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality, biomass | NOEC | 52 | days | 28 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 22 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality, wet weight | NOEC | 28 | days | 27 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 10.42 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 16.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | wet biomass | EC10 | 52 | days | 39.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | overall survival | EC10 | 52 | days | 49.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | dry biomass | EC10 | 52 | days | 38.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 3.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 3.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | all other endpoints covered (see EC10 resul | NOEC | 52 | days | 59 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | length, wet weight | NOEC | 52 | days | 28.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 10.89 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 21 | days | 37 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | growth, mean dry weight | NOEC | 7 | days | 23.2 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 7 | days | 23.2 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 4 | days | 54.7 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 15 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | weight | EC10 | 30 | days | 10 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 3.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | Calfee RD, Little EE, Puglis HJ, Scott E, Brumbaugh WG, Mebane CA | Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures | Environmental Toxicology and Chemistry 33(10):2259-2272 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas (Fathead minnow) | survival and hatch rate and tail movements | NOEC | 2 | days | 338 | μg/L [Cu] | ○ | 0.6 to 621 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Scudder BC, Carter JL, & Leland HV | Effects of copper on development of the fathead minnow, Pimephales promelas Rafinesque | Aquat Toxicol, 12 | 2022/01/18 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | wet weight | EC10 | 28 | days | 13 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 28 | days | 25 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 28.19 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 19.53 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 12.83 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | egg production rate and tail movements | MATC | 32 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Pickering Q, Brungs W, & Gast M | Effect of exposure time and copper concentration on reproduction of the fathead minnow (Pimephales promelas) | Water Res, 11 | 2022/01/18 | ||||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | length | EC10 | 52 | days | >59 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | survival and hatch rate and tail movements | LOEC | 2 | days | 621 | μg/L [Cu] | ○ | 0.6 to 621 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Scudder BC, Carter JL, & Leland HV | Effects of copper on development of the fathead minnow, Pimephales promelas Rafinesque | Aquat Toxicol, 12 | 2022/01/18 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality, biomass | NOEC | 21 | days | 29 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | all endpoints covered (see EC10 results) | NOEC | 52 | days | 24.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | larval fish survival | EC10 | 52 | days | 28.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | wet weight | EC10 | 52 | days | 36 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ng TYT, Chowdhury J, Wood CM | Can the Biotic Ligand Model predict Cu toxicity across a range of pHs in softwater-acclimated rainbow trout? | Environmental Science and Technology 44:6263-6268 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | dry weight | EC10 | 52 | days | 39.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Little EE, Calfee RD, Linder G | Toxicity of copper to early-life stage Kootenai river white sturgeon, Columbia river white sturgeon, and rainbow trout | Archives of Environmental Toxicology and Chemistry 63:400-408 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | length | EC10 | 52 | days | >48.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Little EE, Calfee RD, Linder G | Toxicity of copper to early-life stage Kootenai river white sturgeon, Columbia river white sturgeon, and rainbow trout | Archives of Environmental Toxicology and Chemistry 63:400-408 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | wet biomass | EC10 | 52 | days | 28.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | overall survival | EC10 | 52 | days | 28.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Brachydanio rerio (Zebrafish) | rate and tail movements | 16 | days | 10 EHC (Environmental Health Criteria) | Dave G & Xiu RQ | Toxicity of mercury, copper, nickel, lead, and cobalt to embryos and larvae of zebrafish, Brachydanio rerio | Arch Environ Contam Toxicol, 21 | 2022/01/18 | ||||||||||
| 魚類 | Pimephales promelas | mortality | EC10 | 30 | days | 24 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC10 | 7 | days | 22.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Cyprinodon variegatus | embryo development (length) | NOEC | 32 | days | 57.8 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | study report | 2021/10/25 | ||||||||
| 魚類 | Pimephales promelas | growth rate | NOEC | 187 | days | 69.5 | μg/L [meas. (arithm. mean) Total Cu] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 魚類 | Pimephales promelas | mean number of eggs per female | NOEC | 187 | days | 25.5 | μg/L [meas. (arithm. mean) Total Cu] | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11, 1079-1083 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mean number of eggs per female | NOEC | 97 | days | 23 | μg/L [meas. (arithm. mean) Total Cu] | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11, 1079-1083 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mean number of eggs per female | NOEC | 7 | days | 22.5 | μg/L [meas. (arithm. mean) Total Cu] | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11, 1079-1083 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | growth rate | NOEC | 327 | days | 10.6 | μg/L | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11, 1079-1083 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 327 | days | 10.6 | μg/L | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. & Stephan, C.E. | Chronic Toxicity of Copper to the Fathead Minnow | J. Fish Res. Bd. Canada. 26, 2449-2457 | 2021/10/25 | ||||||
| 魚類 | Cyprinodon variegatus | mortality | NOEC | 32 | days | 109 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | publication | 2021/10/25 | ||||||||
| 魚類 | Pimephales promelas | biomass | EC10 | 30 | days | 6.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Cyprinodon variegatus | number hatched | NOEC | 7 | days | 109 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | publication | 2021/10/25 | ||||||||
| 魚類 | Pimephales promelas | weight | EC10 | 30 | days | 16 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | biomass | EC10 | 30 | days | 15 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | EC10 | 30 | days | 19 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | biomass | EC10 | 30 | days | <9.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 21 | days | 41 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | NOEC | 7 | days | 13.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growt, mean dry biomass | EC10 | 7 | days | 15.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC50 | 7 | days | 24.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC50 | 7 | days | 27.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | reproduction | NOEC | 327 | days | 10.6 | μg/L | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. & Stephan, C.E. | Chronic Toxicity of Copper to the Fathead Minnow | J. Fish Res. Bd. Canada. 26, 2449-2457 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | growth rate | NOEC | 330 | days | 33 | μg/L | 12 ECHA Information on Registered Substances | 2 | Brungs, W.A. et al. | Acute and Chronic Toxicity of Copper to the Fathead Minnow in a Surface Water of Variable Quality | Water Research. 10, 37-43 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC50 | 7 | days | 15.8 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC10 | 7 | days | 9 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | NOEC | 7 | days | 8.7 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC50 | 7 | days | 31 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC50 | 7 | days | 37.4 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 32 | days | 4.8 | μg/L [meas. (arithm. mean)] | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | growth rate | NOEC | 32 | days | 4.8 | μg/L [meas. (arithm. mean)] | 12 ECHA Information on Registered Substances | 2 | Scudder, B. et al. | Effects of Copper on Development of the Fathead Minnow, Pimephales promelas | Aquatic Toxicology. 12, 107-124 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 28 | days | 61 | μg/L [meas. (arithm. mean) mean total copper] | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. | Chronic Toxicity of Copper to Fathead Minnows (Pimphales promelas) | Water Research. 2, 215-223 | 2021/10/25 | ||||||
| 魚類 | Cyprinodon variegatus | embryo development (weight) | NOEC | 32 | days | 57.8 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | study report | 2021/10/25 | ||||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 330 | days | 33 | μg/L | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. | Chronic Toxicity of Copper to Fathead Minnows (Pimphales promelas) | Water Research. 2, 215-223 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 7 | days | 55.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 7 | days | 11.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC10 | 7 | days | >11.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight and mean dry biomas | NOEC | 7 | days | 11.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | weight | EC10 | 30 | days | <4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | EC10 | 30 | days | 19 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | number of eggs/spawn | NOEC | 270 | days | 66 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. & Stephan, C.E. | Chronic Toxicity of Copper to the Fathead Minnow | J. Fish Res. Bd. Canada. 26, 2449-2457 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||||||||
| 魚類 | Pimephales promelas | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||||||||
| 魚類 | Fundulus heteroclitus | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | ||||||||||||||
| 魚類 | Pimephales promelas | reproduction | NOEC | 330 | days | 14.5 | μg/L | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. | Chronic Toxicity of Copper to Fathead Minnows (Pimphales promelas) | Water Research. 2, 215-223 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | ||||||||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 7 | days | 29.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC20 | 7 | days | 28.7 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC20 | 7 | days | 23.9 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 7 | days | 41 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 47.13 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 28.19 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 19.53 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 12.83 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC10 | 7 | days | 25.5 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 10.89 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Waiwood, K.G. & Beamish, F.W.H. | The effect of copper, hardness and pH on the growth of rainbow trout, Salmo gairdneri | Journal of Fish Biology 13, 591-598 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC10 | 7 | days | 18.9 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | ||||||||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | growth rate | NOEC | 78 | days | 16 | μg/L [meas. (arithm. mean)] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | growth rate | NOEC | 60 | days | 2.2 | μg/L [meas. (arithm. mean)] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | bioùass | EC20 | 52 | days | 32 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Seim WK et al. | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously or intermittently exposed to copper. | Can J Fish Aquat Sci 41(3): 433-438 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC20 | 52 | days | 30 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | U.S. EPA | Aquatic life ambient freshwater quality criteria – Copper, 2007 Revision | EPA-822-R-07-001, Feb 2007 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | larval fish survival | EC10 | 52 | days | 54.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | wet weight | EC10 | 52 | days | 47.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | dry weight | EC10 | 52 | days | 45.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 17 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | aquatic mollusc: Crassostreas gigas | Embryo development | NOEC | 24 | hours | 10.42 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC10 | 7 | days | 18.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | NOEC | 7 | days | 15.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC10 | 7 | days | 22 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC50 | 7 | days | 44.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | NOEC | 7 | days | 15.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC10 | 7 | days | 19.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC50 | 7 | days | 35.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 7 | days | 13.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC10 | 7 | days | 13.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC10 | 7 | days | 21 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | NOEC | 7 | days | 13 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | weight | EC10 | 30 | days | 8.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | NOEC | 7 | days | 8.7 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC10 | 7 | days | 10.1 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 7 | days | >12.8 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | NOEC | 7 | days | 8.7 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growt, mean dry biomass | EC10 | 7 | days | 10.2 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC50 | 7 | days | 12.8 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 7 | days | >11.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 4 | days | 22.9 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | NOEC | 7 | days | 23.2 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 7 | days | >24 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Adult bluegill survival and reproduction | LOEC | 22 | months | 162 | μg/L [Cu] | ○ | 12 to 162 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Benoit DA | Chronic effects of copper on survival, growth, and reproduction of the bluegill (Lepomis macrochirus) | Trans Am Fish Soc, 104 | 2022/01/18 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | standing crop | LOEC | 32 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | McKim JM, Eaton JG, & Holcombe GW | Metal toxicity of embryos and larvae of eight species of freshwater fish: II. Copper | Bull Environ Contam Toxicol, 19 | 2022/01/18 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | survival, growth, and reproduction | NOEC | 11 | months | 10.6 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Mount DI & Stephen C | Chronic toxicity of copper to fathead minnow (Pimephales promelas) in soft water | Fish Res Board Can, 26 | 2022/01/18 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | survival, growth, and reproduction | LOEC | 11 | months | 18.4 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Mount DI & Stephen C | Chronic toxicity of copper to fathead minnow (Pimephales promelas) in soft water | Fish Res Board Can, 26 | 2022/01/18 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | reproduction survival | EC0 | 11 | months | 14～15 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Mount DI | Chronic toxicity of copper to fathead minnows (Pimephales promelas, Rafinesque) | Water Res, 2 | 2022/01/18 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | reproduction survival | EC100 | 11 | months | 32～34 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Mount DI | Chronic toxicity of copper to fathead minnows (Pimephales promelas, Rafinesque) | Water Res, 2 | 2022/01/18 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | egg production rate and tail movements | LOEC | 37 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Pickering Q, Brungs W, & Gast M | Effect of exposure time and copper concentration on reproduction of the fathead minnow (Pimephales promelas) | Water Res, 11 | 2022/01/18 | ||||||||
| 魚類 | Cyprinus carpio (Carp) | whole-body sodium and calcium, larval mortality and larval deformation | LOEC | 50.8 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Stouthart XJHX, Haans JLM, Lock RAC, & Wendelaar Bonga SE | Effects of water pH on copper toxicity to early life stages of the common carp (Cyprinus carpio) | Environ Toxicol Chem, 15(3) | 2022/01/18 | ||||||||
| 魚類 | Cyprinus carpio (Carp) | egg mortality, larval heart rate and tail movement or whole-body potassium and magnesium content | NOEC | >=19.1 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Stouthart XJHX, Haans JLM, Lock RAC, & Wendelaar Bonga SE | Effects of water pH on copper toxicity to early life stages of the common carp (Cyprinus carpio) | Environ Toxicol Chem, 15(3) | 2022/01/18 | ||||||||
| 魚類 | Cyprinus carpio (Carp) | egg mortality, heart rate and tail movements | LOEC | 50.8 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Stouthart XJHX, Haans JLM, Lock RAC, & Wendelaar Bonga SE | Effects of water pH on copper toxicity to early life stages of the common carp (Cyprinus carpio) | Environ Toxicol Chem, 15(3) | 2022/01/18 | ||||||||
| 魚類 | Cyprinus carpio (Carp) | whole-body content of potassium, sodium, magnesium, and calcium rate and tail movements | LOEC | 19.1 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Stouthart XJHX, Haans JLM, Lock RAC, & Wendelaar Bonga SE | Effects of water pH on copper toxicity to early life stages of the common carp (Cyprinus carpio) | Environ Toxicol Chem, 15(3) | 2022/01/18 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | reproduction rate and tail movements | NOEC | >=100 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Pickering Q, Brungs W, & Gast M | Effect of exposure time and copper concentration on reproduction of the fathead minnow (Pimephales promelas) | Water Res, 11 | 2022/01/18 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Growth and survival | LOEC | 11 | months | 95 | μg/L [Cu] | ○ | 10 EHC (Environmental Health Criteria) | Mount DI | Chronic toxicity of copper to fathead minnows (Pimephales promelas, Rafinesque) | Water Res, 2 | 2022/01/18 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | growth, abnormalities rate and tail movements | LOEC | 28 | days | <=61 | μg/L [Cu] | ○ | 0.6 to 621 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Scudder BC, Carter JL, & Leland HV | Effects of copper on development of the fathead minnow, Pimephales promelas Rafinesque | Aquat Toxicol, 12 | 2022/01/18 | |||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 28 | days | 128 | μg/L [Cu] | ○ | 0.6 to 621 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Scudder BC, Carter JL, & Leland HV | Effects of copper on development of the fathead minnow, Pimephales promelas Rafinesque | Aquat Toxicol, 12 | 2022/01/18 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC20 | 28 | days | 39 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Schaefer H et al. | Biotests using unicellular algae and ciliates for predicting long-term effects of toxicants | Ecotoxicol Environ Saf 27: 64-81 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | dry weight | EC20 | 28 | days | 43 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Schaefer H et al. | Biotests using unicellular algae and ciliates for predicting long-term effects of toxicants | Ecotoxicol Environ Saf 27: 64-81 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC20 | 52 | days | 36 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | U.S. EPA | Aquatic life ambient freshwater quality criteria – Copper, 2007 Revision | EPA-822-R-07-001, Feb 2007 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas (Fathead minnow) | embryos with abnormalities rate and tail movements | LOEC | 2 | days | 338 | μg/L [Cu] | ○ | 0.6 to 621 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Scudder BC, Carter JL, & Leland HV | Effects of copper on development of the fathead minnow, Pimephales promelas Rafinesque | Aquat Toxicol, 12 | 2022/01/18 | |||||
| 魚類 | Pimephales promelas (Fathead minnow) | survival | LOEC | 28 | days | 113 | μg/L [Cu] | ○ | 0.6 to 621 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Scudder BC, Carter JL, & Leland HV | Effects of copper on development of the fathead minnow, Pimephales promelas Rafinesque | Aquat Toxicol, 12 | 2022/01/18 | |||||
| 魚類 | Lepomis macrochirus (Bluegill) | larvae growth | NOEC | 90 | days | 77 | μg/L [Cu] | ○ | 12 to 162 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Benoit DA | Chronic effects of copper on survival, growth, and reproduction of the bluegill (Lepomis macrochirus) | Trans Am Fish Soc, 104 | 2022/01/18 | |||||
| 魚類 | Lepomis macrochirus (Bluegill) | larvae survival | LOEC | 90 | days | 40 | μg/L [Cu] | ○ | 12 to 162 μg Cu/litre | 10 EHC (Environmental Health Criteria) | Benoit DA | Chronic effects of copper on survival, growth, and reproduction of the bluegill (Lepomis macrochirus) | Trans Am Fish Soc, 104 | 2022/01/18 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 52 | days | 30 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Pesch C. E., Schauer, P.S., Balboni, M.A. | Effect of diet on copper toxicity to Neanthes arenaceodentata | NTIS PB 87-167128. pp. 369-383. In: T.M. Poston and R. Purdy (eds.). ASTM Special Technical Publication N°921: Aquatic Toxicology and Environmental Fate, Vol. 9. A Symposium Amer. Soc. Test. Mater. Philadelphia, PA, USA, 530 p. | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 28 | days | 34 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 21 | days | 31 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 52 | days | 34 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10, pp. 2454-2465, 2003 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC20 | 21 | days | 43 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Pesch C. E., Schauer, P.S., Balboni, M.A. | Effect of diet on copper toxicity to Neanthes arenaceodentata | NTIS PB 87-167128. pp. 369-383. In: T.M. Poston and R. Purdy (eds.). ASTM Special Technical Publication N°921: Aquatic Toxicology and Environmental Fate, Vol. 9. A Symposium Amer. Soc. Test. Mater. Philadelphia, PA, USA, 530 p. | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC20 | 21 | days | 36 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | LaBreche, T.M.C. et al. | Copper Toxicity to Larval Mercenaria mercenaria (hard clam) | Environ Toxicol Chem., 21 (4), 760-766 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC20 | 21 | days | 47 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | WHO | Environmental Health Criteria (EHC) 200, Copper | 2021/10/25 |