【注意事項】
* 生態影響に係る有害性情報更新日が2019年9月以前はRead-acrossデータに○を記載しておらず、被験物質が標記の物質ではない可能性がある。
**各情報源における信頼性評価スコアの定義は下記のとおりである。
| 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) | 毒性値(単位)種別 | 試験中の 被験物質 濃度測定 あり：○ なし：× |
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 | toxicity unit type | Read-across* | QSAR | GLP | measurement of the test material |
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 | Raphidocelis subcapitata | Population/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 solitaria | Population/Population changes, general | EC100 | 8～10 | 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 | Raphidocelis subcapitata | Population/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 | Anabaena lemmermannii | Population/Population changes, general | EC100 | 8～10 | 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 | Chlorella vulgaris | Population/Abundance | 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 | Scenedesmus quadricauda | Population/Population changes, general | EC100 | 8～10 | 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 | Raphidocelis subcapitata | Mortality/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 | Anabaena doliolum | Mortality/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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Chlorella vulgaris | Population | IC50 | 7 | days | 19.2 | μmol/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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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. | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Population | IC50 | 7 | days | 14 | μmol/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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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. | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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. | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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) | 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) | 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 | 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) | biomass | EC50 | 72 | hours | 163 | 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 | 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 | 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) | 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) | 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) | 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 | 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) | 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) | 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 | 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) | 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 | 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) | 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) | 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) | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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) | 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 | 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 | 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 | 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) | 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) | 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) | 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) | 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) | 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) | 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) | 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 | 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 | 245 | 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 | 108 | 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) | 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 | 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) | 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) | 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) | 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 | 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) | 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) | 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 | Selenastrum capricornutum | growth inhibition | EC50 | 72 | hours | 47 | μg/L | ○ | 10 EHC (Environmental Health Criteria) | Nyholm | 2022/02/08 | ||||||||
| 藻類 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Population growth rate | EC50 | 96 | hours | 274.022 | μg/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 | Raphidocelis subcapitata | Population/Abundance | 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 | 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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 | Chlorella vulgaris | Population/Population 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 | Population/Population growth rate | EC50 | 72 | hours | 39.9 | μg/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 | Population/Abundance | 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 | Chlorella vulgaris | Population/Population growth rate | EC50 | 72 | hours | 37.3 | μg/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 | Population/Population growth rate | EC50 | 72 | hours | 34.6 | μg/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 | Population/Population change (change in N/change in time) | 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 | Population/Population change (change in N/change in time) | 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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 | Chlorella vulgaris | Population/Population 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 | Chlorella vulgaris | Population/Population growth rate | EC50 | 72 | hours | 35 | μg/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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Scenedesmus acutus var. acutus | Population/Abundance | EC50 | 24 | hours | 2.59 | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Scenedesmus acutus var. acutus | Population/Abundance | EC50 | 144 | hours | 0.48 | 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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Population change (change in N/change in time) | 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 | Chlorella pyrenoidosa | Population/Abundance | EC50 | 168 | hours | 0.56 | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Chlorella vulgaris | Population/Population growth rate | EC50 | 72 | hours | 38.6 | μg/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 | Population/Abundance | 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 | Scenedesmus acutus var. acutus | Population/Abundance | EC50 | 120 | hours | 0.55 | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 pyrenoidosa | Population/Abundance | EC50 | 96 | hours | 1.01 | 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 | Population/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 | Scenedesmus acutus var. acutus | Population/Abundance | EC50 | 168 | hours | 0.49 | 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 | Phaeodactylum tricornutum | Population/Population 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 | Skeletonema costatum | Population/Population changes, general | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Scenedesmus acutus var. acutus | Population/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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Population/Population change (change in N/change in time) | 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 | Population/Abundance | 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 | Population/Population change (change in N/change in time) | 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 | Population/Abundance | 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 | Chlorella vulgaris | Growth/Growth, general | 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 | Chlorella vulgaris | Population/Population growth rate | EC50 | 72 | hours | 7.8 | μg/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 | Population/Population growth rate | EC50 | 72 | hours | 16.5 | μg/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 | Population/Population change (change in N/change in time) | 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 | Scenedesmus acutus var. acutus | Population/Abundance | EC50 | 72 | hours | 0.66 | 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 | Population/Population growth rate | EC50 | 72 | hours | 36.5 | μg/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 | Population/Abundance | 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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 saccharophila | Population/Abundance | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Population change (change in N/change in time) | 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 | Chlorella vulgaris | Population/Population 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Population change (change in N/change in time) | 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 | Scenedesmus acutus var. acutus | Population/Abundance | EC50 | 96 | hours | 0.73 | 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 | Phaeodactylum tricornutum | Population/Population 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 | Raphidocelis subcapitata | Population/Population 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Dunaliella tertiolecta | Population/Population changes, general | 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/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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 | Chlorella vulgaris | Population/Population growth rate | EC50 | 96 | hours | 4.83 | 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 | Population/Population change (change in N/change in time) | 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 | Phaeodactylum tricornutum | Population/Population 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 | 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 | Chlorella pyrenoidosa | Population/Abundance | EC50 | 48 | hours | 1.24 | 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 | Population/Abundance | 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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 | Raphidocelis subcapitata | Population/Population change (change in N/change in time) | 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 | Population/Abundance | 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 | Dunaliella tertiolecta | Population/Population changes, general | 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 | Phaeodactylum tricornutum | Population/Population growth rate | EC50 | 96 | hours | 409.12 | μg/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 | Population/Population change (change in N/change in time) | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Chlorella saccharophila | Population/Population growth rate | LC50 | 12～14 | days | 1.98 | 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 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 pyrenoidosa | Population/Abundance | EC50 | 72 | hours | 1.14 | 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 | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Population change (change in N/change in time) | 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 | Chlorella saccharophila | Population/Population growth rate | LC50 | 12～14 | days | 15.88 | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Chlorella vulgaris | Population/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 | Raphidocelis subcapitata | Population/Abundance | 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 protothecoides | Population/Population growth rate | LC50 | 12～14 | days | 31.77 | 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 | Population/Population change (change in N/change in time) | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | 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 | Raphidocelis subcapitata | Population/Population growth rate | EC50 | 96 | hours | 381.153 | μg/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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 | Phaeodactylum tricornutum | Population/Population growth rate | EC50 | 96 | hours | 279.241 | μg/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 | 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 | 987 | μg/L | meas. (arithm. mean) dissolved | ○ | 12 ECHA Information on Registered Substances | 2 | 2021/10/25 | |||||||
| 藻類 | Raphidocelis subcapitata | Population/Population change (change in N/change in time) | 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 | Dunaliella tertiolecta | Population/Population changes, general | 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 | 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 | Scenedesmus quadricauda | Population/Population 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 | Raphidocelis subcapitata | Population/Population change (change in N/change in time) | 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 | Thalassiosira pseudonana | Population/Population change (change in N/change in time) | 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 | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Navicula incerta | Population/Population change (change in N/change in time) | 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 | Scenedesmus acutus var. acutus | Population/Abundance | EC50 | 72 | hours | 14.31 | μM | × | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Chlorella pyrenoidosa | Population/Abundance | EC50 | 24 | hours | 1.45 | 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 | Population/Population change (change in N/change in time) | 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 | Scenedesmus acutus var. acutus | Population/Abundance | EC50 | 48 | hours | 0.41 | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Chlorella pyrenoidosa | Population/Abundance | EC50 | 120 | hours | 0.87 | 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 | Population/Abundance | 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 | Chlorella saccharophila | Mortality/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 | Chlorella protothecoides | Population/Population growth rate | LC50 | 12～14 | days | 1.98 | 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 vulgaris | Population/Abundance | 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 | Population/Abundance | 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 | 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 | Raphidocelis subcapitata | Population/Population change (change in N/change in time) | 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 | Chlorella pyrenoidosa | Population/Abundance | EC50 | 144 | hours | 0.71 | 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 | 72 | hours | 333 | μg/L | meas. (arithm. mean) dissolved | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 99 | 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 | 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 | 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) | 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 | 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) | 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 | 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 | 773 | 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 | EC50 | 72 | hours | 36.9 | 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) | 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) | 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 | 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 | 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 | 33.9 | μg/L | meas. (initial) element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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) | 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 | 230 | μg/L | meas. (arithm. mean) dissolved | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 17.9 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 94.7 | 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) | 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) | 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) | 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) | 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 | 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 | 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) | 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) | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Scenedesmus acutus var. acutus | Population/Abundance | LOEC | 24～268 | hours | 0.36 | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Biomass | LOEC | 2～12 | 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 | Phaeodactylum tricornutum | Population/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 | Anabaena doliolum | Population/Population 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Chlorella vulgaris | Population/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 | Raphidocelis subcapitata | Population/Abundance | 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 | Navicula tripunctata | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Chlorella vulgaris | Population/Population 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 | Navicula cryptocephala | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Biomass | LOEC | 30～57 | 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 | Population/Abundance | 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 | Dunaliella tertiolecta | Population/Population changes, general | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Scenedesmus sp. | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Chlorella vulgaris | Population/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 | Chlorella vulgaris | Population/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 | Population/Abundance | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Navicula sp. | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Population 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 seminulum | Population/Biomass | NOEC | 30～57 | 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 | Population/Population 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 | Navicula sp. | Population/Abundance | 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 | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | 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 | Scenedesmus sp. | Population/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 | Chlorella vulgaris | Population/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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Phaeodactylum tricornutum | Population/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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Population 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 | Scenedesmus sp. | Population/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 | Population/Population 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 | Anabaena doliolum | Population/Population 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Population/Population 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 | Population/Biomass | NOEC | 2～12 | 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 | Population/Population 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 pyrenoidosa | Population/Abundance | LOEC | 24～168 | hours | 0.36 | 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 | Population/Abundance | 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 | Raphidocelis subcapitata | Population/Abundance | 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 | Population/Abundance | 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 | Navicula tripunctata | Population/Abundance | 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 | Chlorella vulgaris | Population/Population 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 | Navicula cryptocephala | Population/Abundance | 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 | Scenedesmus quadricauda | Population/Biomass | LOEC | 30～57 | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | Population/Abundance | 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 | 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) | 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 | 15.7 | 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 | 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 | 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 | 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 | 49.4 | μg/L | meas. (arithm. mean) dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 53.3 | 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 | |||||||
| 甲殻類 | Nitocra spinipes | Mortality/Mortality | LOEC | 6 | days | 440 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 magna | Biochemical | LOEC | 4 | days | 4.212 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Daphnia magna | Biochemical | NOEC | 4 | days | 4.212 | 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 | 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 | 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 | 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 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 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 | 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 | 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 | 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 | 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 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 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 | <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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | <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 | 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 | 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 | 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 | 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 | 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 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 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 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 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 | 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 | 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 | 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 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 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 | 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 | 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 | 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 | 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 | 2.67 | 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 | 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 | 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 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 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | >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 | 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 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 | 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 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 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 | 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 | 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 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 sp. Ceriodaphnia cornuta | Reproduction | NOEC | 33 | days | 4.83 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 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 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 | 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 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | Ceriodaphnia sp. Ceriodaphnia cornuta | Reproduction | LOEC | 2.61 | days | 3.2 | 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 | 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 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 | 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 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 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 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 | 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 | 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 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 | 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 | 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 | 4 | days | 11.172 | 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 | 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 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 | 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 | 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 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 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 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 | 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 | 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 | 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 | 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 | 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 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 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 | 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 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 | 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 | Ceriodaphnia sp. Ceriodaphnia cornuta | Physiology | EC50 | 1 | days | 0.0809 | 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 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 sp. Ceriodaphnia cornuta | Growth | NOEC | 33 | days | 4.83 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 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 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 | 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 | 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 | 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 | Physiology | LOEC | 4 | days | 4.212 | 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 | 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 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 | 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 | 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 | 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 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 | 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 | 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 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 | 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 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 | 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 | 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 | 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 | 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 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 | 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 | 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 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 | 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 | 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 | 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 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 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 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 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 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 | 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 | Ceriodaphnia dubia | Mortality | LC50 | 7 | days | 7.5 | 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 | >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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 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 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 | 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 | Ceriodaphnia sp. Ceriodaphnia cornuta | Accumulation | LOEC | 1 | days | 0.01 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 4 | days | 11.172 | 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 | 4.212 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 1.3 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 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 | 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 | 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 | 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 | 4 | days | 4.212 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | Ceriodaphnia dubia | Mortality | EC50 | 7 | days | 7.5 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 magna | Physiology | LOEC | 4 | days | 4.212 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 5.3 | 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 | Reproduction | IC50 | 7 | days | 5.3 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Daphnia pulex | Mortality/Survival | NOEC | 14 | days | 6.25 | μg/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 | Intoxication/Immobile | EC50 | 96 | hours | 352 | μg/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/Survival | LOEL | 10～15 | 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 | Mortality/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/Survival | NOEC | 4 | days | 6.25 | μg/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 | Crassostrea gigas | Intoxication/Immobile | 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 | Daphnia magna | Mortality/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 | Mortality/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 | Nitocra spinipes | Mortality/Mortality | NOEC | 6 | days | 220 | 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 | 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 | Daphnia magna | Mortality/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 | Mortality/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 | Mytilus edulis | Mortality/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 | Palaemonetes pugio | Mortality/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 | Intoxication/Immobile | EC50 | 96 | hours | 9.28 | μg/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 | Behavior/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 | Daphnia magna | Mortality/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 | Palaemonetes pugio | Development/Stage | NOEL | >90～<95 | 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 | Mortality/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 | Palaemonetes pugio | Development/Stage | LOEL | >18～<20 | 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 | Mytilus edulis | Mortality/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 | Intoxication/Immobile | EC50 | 10～12 | 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 | Palaemonetes pugio | Mortality/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 | Nitocra spinipes | Development/Normal | NOEC | 6 | days | 49 | 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 | Daphnia magna | Mortality/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 | Crassostrea gigas | Intoxication/Immobile | 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 | Crassostrea gigas | Intoxication/Immobile | 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 | Growth/Growth, general | 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 | Palaemonetes pugio | Mortality/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 | Mortality/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 | Palaemonetes pugio | Mortality/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 pulex | Mortality/Survival | NOEC | 8 | days | 6.25 | μg/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 | Daphnia magna | Behavior/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 | Behavior/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 | Behavior/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 magna | Behavior/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 | Mytilus edulis | Mortality/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 | Behavior/Valve closure | LOEL | 0～48 | 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 | Nitocra spinipes | Development/Normal | LOEC | 6 | days | 110 | 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 | Daphnia magna | Mortality/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 | Behavior/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 | Mytilus edulis | Behavior/Valve closure | NOEL | 0～48 | 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 | Development/Developmental changes, general | 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 | Mortality/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/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/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 | Mytilus edulis | Mortality/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 | Daphnia magna | Intoxication/Immobile | EC50 | 96 | hours | 78.9 | μg/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/Survival | NOEL | 10～15 | 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 | Mytilus edulis | Mortality/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 | Daphnia magna | Behavior/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 | Mytilus edulis | Mortality/Mortality | NR-LETH | 21 | days | 100 | μg/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 | Mytilus edulis | Mortality/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/Mortality | LC50 | 8～10 | 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 | Mytilus edulis | Mortality/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/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 | Mortality/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 | Daphnia pulex | Mortality/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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Ceriodaphnia dubia | Mortality | LC50 | 7 | days | 70.5 | μg/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 | 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 | 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 | 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 | Biochemical | LOEC | 4 | days | 11.172 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Ceriodaphnia dubia | Mortality | LOEL | 7 | days | 74.7 | μg/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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | <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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Behavior | LOEL | 7 | days | 74.7 | μg/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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 45.3 | μg/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 | 5.3 | 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 | IC25 | 7 | days | 14.4 | μg/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 | IC25 | 7 | days | 2.5 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 45.3 | μg/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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Ceriodaphnia dubia | Accumulation | NOEL | 7 | days | 163.4 | μg/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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 5.3 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Biochemical | LOEC | 4 | days | 4.212 | 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 | LOEC | 4 | days | 4.212 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Ceriodaphnia dubia | Reproduction | LOEL | 7 | days | 15.9 | μg/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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Biochemical | LOEC | 4 | days | 4.212 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Biochemical | LOEC | 4 | days | 4.212 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | NOEC | 4 | days | 4.212 | 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 | NOEC | 4 | days | 4.212 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | LOEC | 4 | days | 4.212 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 45.6 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Ceriodaphnia dubia | Mortality | EC50 | 7 | days | 70.5 | μg/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 | 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 | 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 | 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 | 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 | 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 | 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 | 7 | days | 7.5 | 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 | 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 | 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 | 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 | Ceriodaphnia dubia | Mortality | EC50 | 7 | days | 7.5 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | <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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Daphnia magna | Biochemical | LOEC | 4 | days | 11.172 | 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 | 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 | Physiology | LOEC | 4 | days | 4.212 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 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 | 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 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 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 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 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 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 | 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 | Ceriodaphnia sp. Ceriodaphnia cornuta | Reproduction | NOEC | 33 | days | 4.83 | 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 | 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 | 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 | 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 | 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 | Ceriodaphnia sp. Ceriodaphnia cornuta | Reproduction | NOEC | 33 | days | 4.83 | 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 | 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 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 | 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 | 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 | 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 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 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 | 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 | 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 | 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 | 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 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 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 | 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 | 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 | 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 | 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 | 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 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | mortality | LC50 | 48 | hours | 28 | μg/L | meas. dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | LC50 | 48 | hours | 28 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 10 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 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 | 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 | 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 | 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 | 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 | LC50 | 48 | hours | 32 | μg/L | meas. dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 37 | μg/L | meas. dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Daphnia magna | Mortality/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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >0～41.8 | μg/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/Mortality | LC50 | 48 | hours | 58.1 | μg/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 | Mortality/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 | Daphnia longispina | Mortality/Mortality | LC50 | 48 | hours | 75.1 | μg/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/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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 | Intoxication/Immobile | 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 | Behavior/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 | Ceriodaphnia dubia | Mortality/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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/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 | Intoxication/Immobile | 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/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 | Ceriodaphnia dubia | Mortality/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 | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/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 | Tisbe battagliai | Mortality/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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Mortality/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Ceriodaphnia dubia | Mortality/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 magna | Mortality/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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Daphnia pulex | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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/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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Mortality/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 | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/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 | Nitocra spinipes | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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 | Intoxication/Immobile | 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 | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 magna | Mortality/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 | Daphnia magna | Mortality/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 reticulata | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Mortality/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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | EC50 | 48 | hours | 14.5 | μg/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 | Intoxication/Immobile | 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 | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/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 | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >300～400 | μg/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 | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/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/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 | Mortality/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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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/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 | Daphnia magna | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 hyalina | Mortality/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 | Holmesimysis costata | Mortality/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 magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Tisbe battagliai | Mortality/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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 longispina | Mortality/Mortality | LC50 | 48 | hours | 25.2 | μg/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 | Intoxication/Immobile | 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 | mobility | EC50 | 48 | hours | 152 | μg/L | meas. (arithm. mean) dissolved | 12 ECHA Information on Registered Substances | 2 | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia magna | Intoxication/Immobile | 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 | mobility | EC50 | 48 | hours | 210 | μg/L | meas. (arithm. mean) dissolved | 12 ECHA Information on Registered Substances | 2 | 2021/10/25 | ||||||||
| 甲殻類 | Ceriodaphnia dubia | Mortality/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 | Ceriodaphnia dubia | Mortality/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 cornuta | Intoxication/Immobile | EC50 | 24 | hours | 0.0000000809 | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Crassostrea virginica | Development/Abnormal | 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 | Daphnia magna | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Mortality/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 | Mortality/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 | Mytilus edulis | Behavior/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 | 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 | 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 pulex | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | EC50 | 48 | hours | 415 | μg/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 | Daphnia magna | Mortality/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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 pulex | Mortality/Survival | NOEC | 12 | days | 6.25 | μg/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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/Mortality | LC50 | 48 | hours | >67.4～100 | μg/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/Survival | NOEC | 16 | days | 6.25 | μg/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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Mortality/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 | Intoxication/Immobile | 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 | Mortality/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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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/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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/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 longispina | Mortality/Mortality | LC50 | 48 | hours | 26.1 | μg/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 | Mortality/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 | Intoxication/Immobile | 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 pulex | Intoxication/Immobile | 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 | Daphnia magna | Mortality/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/Mortality | LC50 | 48 | hours | >200～300 | μg/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/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 magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Daphnia pulex | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Mortality/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 | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Daphnia pulex | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Mortality/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 | Intoxication/Immobile | 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 pulex | Intoxication/Immobile | 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 magna | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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/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 | Daphnia longispina | Mortality/Mortality | LC50 | 48 | hours | 38 | μg/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 | Intoxication/Immobile | 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 | Daphnia magna | Mortality/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Intoxication/Immobile | 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 | Tisbe battagliai | Mortality/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/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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/Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/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 | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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/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 | Mortality/Mortality | EC50 | 48 | hours | 17 | μg/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/Mortality | EC50 | 48 | hours | 260 | μg/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 | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Daphnia magna | Mortality/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/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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/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/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | EC50 | 48 | hours | 634 | μg/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Behavior/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 | Daphnia magna | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Daphnia magna | Mortality/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 longispina | Mortality/Mortality | LC50 | 48 | hours | 40.4 | μg/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 | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >107.8～200 | μg/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 | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | 67.4 | μg/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 | Intoxication/Immobile | 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 magna | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Ceriodaphnia dubia | Mortality/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 | Intoxication/Immobile | 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 | Crassostrea gigas | Mortality/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 | Daphnia magna | Mortality/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 | 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 | Strongylocentrotus purpuratus | Development/Developmental changes, general | 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 | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/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/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/Mortality | LC50 | 48 | hours | >67.4～100 | μg/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/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 | Ceriodaphnia dubia | Mortality/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 | Crassostrea virginica | Development/Developmental changes, general | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Farfantepenaeus duorarum | Mortality/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 | Daphnia pulex | Intoxication/Immobile | 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 pulex | Intoxication/Immobile | 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/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 | Mercenaria mercenaria | Growth/Growth, general | 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 | Chironomus tentans | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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/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 | Daphnia magna | Intoxication/Immobile | 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 | Chironomus riparius | Mortality/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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Mortality/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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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/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 | Daphnia magna | Intoxication/Immobile | 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 longispina | Mortality/Mortality | LC50 | 48 | hours | 318.6 | μg/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/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 magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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/Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/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/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 pulex | Mortality/Survival | NOEC | 2 | days | 6.25 | μg/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | 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 pulex | Intoxication/Immobile | 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 | Americamysis bahia | Mortality/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 magna | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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 | Intoxication/Immobile | 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/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 | Daphnia magna | Mortality/Mortality | NR-ZERO | 48 | hours | 186 | μg/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 | Intoxication/Immobile | 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/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/Mortality | NR-ZERO | 24 | hours | 135 | μg/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 | Daphnia magna | Intoxication/Immobile | 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 | Chironomus riparius | Mortality/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 | Daphnia pulex | Mortality/Survival | NOEC | 10 | days | 6.25 | μg/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 | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | 41.8 | μg/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/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/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/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 | Crassostrea virginica | Mortality/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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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 | Chironomus riparius | Mortality/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 tentans | Mortality/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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | 108.7 | μg/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 | Intoxication/Immobile | 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 | Mortality/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 | Intoxication/Immobile | 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 | Chironomus riparius | Growth/Growth, general | 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 | Daphnia longispina | Mortality/Mortality | LC50 | 48 | hours | 38.3 | μg/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Mortality/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 | Intoxication/Immobile | 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 longispina | Mortality/Mortality | LC50 | 48 | hours | 18 | μg/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 | Intoxication/Immobile | 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 | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Daphnia longispina | Mortality/Mortality | LC50 | 48 | hours | 58.4 | μg/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/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 | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Mortality/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 | Daphnia longispina | Mortality/Mortality | LC50 | 48 | hours | 59 | μg/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 | 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 | Crassostrea gigas | Intoxication/Immobile | 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 | 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 | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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 | Tisbe battagliai | Mortality/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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >41.8～67.4 | μg/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/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 | 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 | Daphnia magna | Mortality/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 | Intoxication/Immobile | 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 | Crassostrea gigas | Intoxication/Immobile | 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 | 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 | Dendraster excentricus | Development/Developmental changes, general | 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 | 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 pulex | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/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/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 | Ceriodaphnia dubia | Mortality/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 longispina | Mortality/Mortality | LC50 | 48 | hours | 80.7 | μg/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/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 | Intoxication/Immobile | 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 | 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/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 | Ceriodaphnia dubia | Mortality/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 | Acartia tonsa | Mortality/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | 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 | Crassostrea gigas | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Mortality/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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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/Mortality | LC50 | 48 | hours | >200～300 | μg/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | 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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Crassostrea virginica | Development/Developmental changes, general | 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 | Daphnia magna | Intoxication/Immobile | 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 | Crassostrea gigas | Intoxication/Immobile | 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 | Crassostrea virginica | Development/Developmental changes, general | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | 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 | Mortality/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 | 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 | Behavior/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 | 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 | Intoxication/Immobile | 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 | Ceriodaphnia dubia | Mortality/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 | Ceriodaphnia dubia | Mortality/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 | Intoxication/Immobile | 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 | Daphnia magna | Behavior/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 | Intoxication/Immobile | 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 | Nitocra spinipes | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | 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 | Ceriodaphnia dubia | Mortality/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 | Mortality/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 magna | Intoxication/Immobile | 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 | Tisbe battagliai | Mortality/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 | Crassostrea gigas | Intoxication/Immobile | 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 | Daphnia magna | Mortality/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 | Ceriodaphnia dubia | Mortality/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 magna | Intoxication/Immobile | 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 | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >67.4～108.7 | μg/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | EC50 | 48 | hours | 102 | μg/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 longispina | Mortality/Mortality | LC50 | 48 | hours | 48.5 | μg/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 | 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 | Intoxication/Immobile | 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 | Crassostrea gigas | Intoxication/Immobile | 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 | 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 | Tisbe battagliai | Mortality/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 | Intoxication/Immobile | 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 | 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 | Intoxication/Immobile | 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 | 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 | Strongylocentrotus droebachiensis | Development/Developmental changes, general | 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 | Daphnia magna | Intoxication/Immobile | 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 | 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 | Daphnia magna | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >108.7～200 | μg/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 | Crassostrea gigas | Intoxication/Immobile | 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 | 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 | 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 | 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 | Intoxication/Immobile | 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 | Chironomus riparius | Mortality/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 | Crassostrea gigas | Intoxication/Immobile | 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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | 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 | Intoxication/Immobile | 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 longispina | Mortality/Mortality | LC50 | 48 | hours | 23.7 | μg/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 | Mortality/Mortality | NR-ZERO | 48 | hours | 13 | μg/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/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 | Mortality/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 | Intoxication/Immobile | 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 | Tisbe battagliai | Mortality/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 | Ceriodaphnia dubia | Mortality/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 longispina | Mortality/Mortality | LC50 | 48 | hours | 358.4 | μg/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/Mortality | LC50 | 48 | hours | 23.2 | μg/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/Mortality | LC50 | 48 | hours | 25.8 | μg/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/Mortality | LC50 | 48 | hours | 21.9 | μg/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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Holmesimysis costata | Mortality/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 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 | Intoxication/Immobile | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | 67.4 | μg/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 | Strongylocentrotus purpuratus | Development/Developmental changes, general | 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 | Daphnia pulex | Mortality/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 | Ceriodaphnia dubia | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | 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 | Ceriodaphnia dubia | Intoxication/Immobile | 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/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 | Dendraster excentricus | Development/Developmental changes, general | 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 | Daphnia pulex | Intoxication/Immobile | 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 | Strongylocentrotus droebachiensis | Development/Developmental changes, general | 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 | Daphnia magna | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Intoxication/Immobile | 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 | Mortality/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 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 | Crassostrea gigas | Development/Developmental changes, general | 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 | 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 | 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 | Mytilus edulis | Development/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 | Daphnia magna | Mortality/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 | 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/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 | 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 | Daphnia pulex | Intoxication/Immobile | 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 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 | 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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >300～400 | μg/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 | Crassostrea gigas | Intoxication/Immobile | 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 | Daphnia magna | Mortality/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 | Acartia tonsa | Mortality/Mortality | LC50 | 48 | hours | >108.7～150 | μg/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 | 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 | Intoxication/Immobile | 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 | Mortality/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 | Daphnia longispina | Mortality/Mortality | LC50 | 48 | hours | 95.1 | μg/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 | 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 | Intoxication/Immobile | 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 | 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 | 106 | μg/L | meas. (arithm. mean) dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia longispina | Mortality/Mortality | LC50 | 48 | hours | 20.04 | μg/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 | Crassostrea gigas | Mortality/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/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 | Daphnia magna | Mortality/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 | Ceriodaphnia dubia | Mortality/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 | Crassostrea gigas | Mortality/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/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 | Daphnia magna | Intoxication/Immobile | 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 | Crassostrea virginica | Mortality/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 | Daphnia magna | Intoxication/Immobile | 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 | Tisbe battagliai | Mortality/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 | Intoxication/Immobile | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 332 | 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 | 39 | 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 | 51 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 529 | 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 | 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 | 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 | 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 | mortality | LC50 | 48 | hours | 35 | 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 | Daphnia magna | These observations consistently show that the presence of organic matter decreases the bioavailability, uptake, and ecotoxicity of copper in the aquatic environment | 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 | 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 | 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 | 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 | 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 | 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 | 31 | 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 | 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 | 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 | 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 | 39 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | EC50 | 48 | hours | 7.4 | 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 | 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 | <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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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. 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 | 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 | 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 | 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 | 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 | 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 | mortality | LC50 | 48 | hours | 90 | μg/L | meas. element | ○ | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | see summary | 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 | 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 | see summary | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 44 | μg/L | meas. (initial) element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 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 | 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 | Daphnia ambigua | NOEC | All four species exhibited reductions in survival at concentrations > 40 μg Cu/litre. Instantaneous rate of population growth was affected at > 40 μg Cu/litre for D. ambigua. Daphnia ambigua produced significantly smaller broods at concentrations > 40 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 magna Daphnia pulex | 28 | days | D. pulex populations consistently exceeded D. magna populations when cocultured in the absence of copper or temporary exposures to 10 μg Cu/litre. Exposure to 30 μg Cu/litre severely reduced initial population growth of D. pulex without affecting D. magna. By day 14 D. magna populations were dominant; however, D. pulex population growth was not completely suppressed and by the end of the experiment (28 days) D. pulex had gained population dominance. The reduced size of D. magna suggested that D. pulex was out-competing D. magna for available food. | ○ | 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 pulex | mortality | NOEC | 42 | days | 40 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 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 | 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 | 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 | 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 | 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 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 | |||||||
| 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 | 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 | 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 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 | 5 | 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 | 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 | 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 | 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 | 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 | 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 | Daphnia magna | Dietary copper exposure did not affect the predicitve capacity of the chronic D. magna BLM | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | NOEC | All four species exhibited reductions in survival at concentrations > 40 μg Cu/litre. Daphnia magna exhibited a decrease in the instantaneous rate of population growth at 60 μg Cu/litre; Mean brood size in D. magna was unaffected by copper exposure. | ○ | 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 | 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 | 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 pulex | NOEC | All four species exhibited reductions in survival at concentrations > 40 μg Cu/litre. Instantaneous rate of population growth was affected at > 40 μg Cu/litre for D. pulex. Mean brood size did not decrease in D. pulex until the concentration exceeded 60 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 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 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 | survival | NOEC | 70 | days | 5 | μg/L | Cu | ○ | 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 | All four species exhibited reductions in survival at concentrations > 40 μg Cu/litre. Instantaneous rate of population growth was affected at > 40 μg Cu/litre for D. parvula. Mean brood size did not decrease in D. parvula until the concentration exceeded 60 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 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 | 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 pulex | survival | LOEC | 70 | days | 10 | μg/L | Cu | ○ | 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 | 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 | Mortality/Mortality | EC50 | 21 | days | 98 | μg/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 | 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 | 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 | 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 longispina | Reproduction/Net Reproductive Rate | NOEC | 21 | days | 42.3 | μg/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/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 | Reproduction/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 | Population/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 | 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 | 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 | 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 | 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 | 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 | 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 | Daphnia magna | Reproduction/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 longispina | Population/Population growth rate | LOEC | 21 | days | 156.5 | μg/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 | 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 longispina | Mortality/Mortality | NOEC | 21 | days | 42.3 | μg/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 | ○ | 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 | Population/Population growth rate | EC50 | 21 | days | 90 | μg/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/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 | 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 | Daphnia longispina | Growth/Growth rate | LOEC | 21 | days | 5.5 | μg/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 | ○ | 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 | Population/Population growth rate | LOEC | 21 | days | 9.2 | μg/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 | Population/Population growth rate | EC50 | 21 | days | 227 | μg/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/Mortality | NOEC | 21 | days | 85.2 | μg/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/Hatch | NOEC | 33 | days | 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 | 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 | Intoxication/Immobile | 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 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 | 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 pulex | Reproduction/Progeny counts/numbers | LOEC | 16 | days | 6.25 | μg/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 | 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 magna | Reproduction/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 | Palaemonetes pugio | Reproduction/Progeny counts/numbers | LOEL | >240～<261 | 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 | 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 | Ceriodaphnia cornuta | Reproduction/Progeny counts/numbers | NOEC | 33 | days | 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 pulex | Reproduction/Progeny counts/numbers | NOEC | 12 | days | 6.25 | μg/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 | 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 | 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 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 | Daphnia longispina | Reproduction/Time to first progeny | NOEC | 21 | days | 85.2 | μg/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/Net Reproductive Rate | NOEC | 21 | days | 156.5 | μg/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 | ○ | 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 | Daphnia longispina | Mortality/Mortality | EC50 | 21 | days | 269 | μg/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 | 70.2 | 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 | Population/Population growth rate | NOEC | 21 | days | 85.2 | μg/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 | Population/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 | Daphnia longispina | Reproduction/Net Reproductive Rate | LOEC | 21 | days | 21.3 | μg/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 | 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 longispina | Reproduction/Progeny counts/numbers | NOEC | 21 | days | 156.5 | μg/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 | 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 longispina | Population/Population growth rate | LOEC | 21 | days | 85.2 | μg/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/Net Reproductive Rate | LOEC | 21 | days | 85.2 | μg/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/Mortality | LOEC | 21 | days | 85.2 | μg/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 | Mortality/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 | 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 | 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 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 | Ceriodaphnia dubia | Mortality/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 | Reproduction/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 | 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 | 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 | Mortality/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/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 | 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 | 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/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 | Ceriodaphnia cornuta | Development/Slowed, Retarded, Delayed or Non-development | NOEC | 33 | days | 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/Net Reproductive Rate | EC50 | 21 | days | 216 | μg/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/Net Reproductive Rate | EC50 | 21 | days | 72 | μg/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/Net Reproductive Rate | LOEC | 21 | days | 5.5 | μg/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 | 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 longispina | Growth/Growth rate | EC50 | 21 | days | 90 | μg/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 | 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 longispina | Population/Population growth rate | EC50 | 21 | days | 88 | μg/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/Mortality | EC50 | 21 | days | 87 | μg/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 | 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 | 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 | 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 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 | 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 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 | 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 | Ceriodaphnia dubia | Mortality/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 | Daphnia longispina | Growth/Growth rate | EC50 | 21 | days | 102 | μg/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 | × | 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/Growth rate | EC50 | 21 | days | 356 | μg/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 | Population/Population growth rate | EC50 | 21 | days | 79 | μg/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 | ○ | 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 | 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 | Mortality/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/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 | Ceriodaphnia cornuta | Growth/Growth rate | LOEC | 21 | days | 0.0000032 | 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 | Population/Population growth rate | NOEC | 21 | days | 5.5 | μg/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/Net Reproductive Rate | NOEC | 21 | days | 9.2 | μg/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 | Mortality/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/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/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/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 | 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 | Dendraster excentricus | Reproduction/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 | Daphnia longispina | Growth/Growth rate | LOEC | 21 | days | 5.5 | μg/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/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/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/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 | 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 longispina | Reproduction/Time to first progeny | LOEC | 21 | days | 156.5 | μg/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/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 longispina | Mortality/Mortality | NOEC | 21 | days | 42.3 | μg/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/Mortality | EC50 | 21 | days | 80 | μg/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/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/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 | Mortality/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 longispina | Population/Population growth rate | NOEC | 21 | days | 42.3 | μg/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/Mortality | NOEC | 21 | days | 156.5 | μg/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/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 | Ceriodaphnia cornuta | Reproduction/Time to first progeny | LOEC | 2.61 | days | 0.0000032 | 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/Net Reproductive Rate | EC50 | 21 | days | 80 | μg/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 | 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 | 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 magna | Reproduction/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 | 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 | Ceriodaphnia cornuta | Mortality/Lifespan | NOEC | 33 | days | 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 | Mortality/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 longispina | Growth/Growth rate | LOEC | 21 | days | 5.5 | μg/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 | Mortality/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 longispina | Mortality/Mortality | LOEC | 21 | days | 85.2 | μg/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 | 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 | Mortality/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 pulex | Reproduction/Reproduction, general | 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/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 cornuta | Reproduction/Progeny counts/numbers | NOEC | 33 | days | 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 | 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 | Daphnia longispina | Population/Population growth rate | LOEC | 21 | days | 42.3 | μg/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 | ○ | 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 | 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/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 | 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 | Mortality/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 | 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 | 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/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 | Crassostrea gigas | Reproduction/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 | Daphnia magna | Reproduction/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/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 | Strongylocentrotus purpuratus | Reproduction/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 | Daphnia magna | Reproduction/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 | 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/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 | Mortality/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 | 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 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 | Crassostrea gigas | Reproduction/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 | Daphnia longispina | Reproduction/Net Reproductive Rate | EC50 | 21 | days | 85 | μg/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 | Mortality/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/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 | 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 | Mortality/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/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 | Strongylocentrotus droebachiensis | Reproduction/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 | Reproduction/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 | Strongylocentrotus droebachiensis | Reproduction/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 | 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 | Mortality/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 longispina | Reproduction/Time to first progeny | LOEC | 21 | days | 85.2 | μg/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 | Population/Population growth rate | NOEC | 21 | days | 21.3 | μg/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 | 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 longispina | Mortality/Mortality | LOEC | 21 | days | 156.5 | μg/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 | Strongylocentrotus droebachiensis | Reproduction/Reproduction, general | 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 | Reproduction/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 | reproduction | NOEC | 21 | days | 21.5 | μg/L | 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 | 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 magna | Mortality/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 | 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/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 longispina | Growth/Growth rate | NOEC | 21 | days | 85.2 | μg/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 | Mortality/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 | Mortality/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 | 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 | 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 | 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/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 | Reproduction/Progeny counts/numbers | LOEC | 21 | days | 229.9 | μg/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 | Population/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 | Reproduction/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 | 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 | Daphnia longispina | Mortality/Mortality | LOEC | 21 | days | 229.9 | μg/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 | 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 | Reproduction/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/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/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/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 | 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 | 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 | 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 | Chironomus dilutus | Population/Abundance | NOEC | 21 | days | 58.83 | μg/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 | 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 magna | Mortality/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 | Dendraster excentricus | Reproduction/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 | Daphnia magna | Mortality/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 pulex | Mortality/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 | Strongylocentrotus purpuratus | Reproduction/Reproduction, general | 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 | 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 | 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/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 | 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 | Dendraster excentricus | Reproduction/Reproduction, general | 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 | Reproduction/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 | Ceriodaphnia cornuta | Population/Generation time | LOEC | 33 | days | 0.0000032 | 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 | Mortality/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 | Mortality/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 | Reproduction/Reproduction, general | 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 | Ceriodaphnia cornuta | Reproduction/Number of days between eggs laid or litters | NOEC | 33 | days | 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/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/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 | Mortality/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/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 pulex | Reproduction/Progeny counts/numbers | LOEC | 14 | days | 6.25 | μg/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 | 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 longispina | Reproduction/Net Reproductive Rate | LOEC | 21 | days | 229.9 | μg/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 | 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 | 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 longispina | Growth/Growth rate | EC50 | 21 | days | 160 | μg/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/Growth rate | LOEC | 21 | days | 156.5 | μg/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 | Mortality/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 | 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 | Daphnia magna | Mortality/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/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 | Mortality/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/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 | Crassostrea gigas | Reproduction/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 | Daphnia magna | Reproduction/Reproduction, general | 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 | 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 | Mortality/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 | Reproduction/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 pulex | Reproduction/Progeny counts/numbers | EC50 | 21 | days | 5.11 | μg/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 | 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 | 5.7 | μg/L | meas. (TWA) element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | 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 | 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 | 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 | 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 | 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 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 | 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 pulex | mortality | NOEC | 42 | days | 20 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 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 | after three generation of acclimation, the optimal concentration ranges (from energy reserves and number of offsprings) remained constant between 1 and 35 µg Cu/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 | 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 | With the model, 79% of the toxicity threshold values were predicted within a factor of two | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 | Daphnia magna | reproduction | NOEC | 21 | days | 181 | μg/L | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 106 | μg/L | 12 ECHA Information on Registered Substances | 2 | 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 | 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 | 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 | 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 | 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 | 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 | 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 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 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 | 56.2 | 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 | 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 | 17 | 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 | 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 | 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 | 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 | 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 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 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 | EC10 | 21 | days | 50.2 | 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 | 47 | μg/L | meas. (TWA) element | ○ | 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 | 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 | 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 | 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 | 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 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 | ||||
| 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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) | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 90 | μg | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 36 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | >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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 56 | days | 36 | μg | 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 | μg | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 36 | μg | 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 | μg | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 90 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 14 | days | 36 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 8.1 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 18 | μg | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 90 | μg | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | μg | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 18.1 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | μg | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | μg | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | μg | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 56 | days | 18 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 36 | μg | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | 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 | 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 | 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 | 14 | days | 90 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 36 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | μg | 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 | μg | 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 | μg | 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 | 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 | 2.5 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 36 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 2.5 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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) | 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 | 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 | 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) | 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) | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | Mortality/Mortality | LC50 | >36～<48 | hours | >15～20 | μg/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/Mortality | LC50 | >72～<96 | hours | >10～15 | μg/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/Mortality | LC50 | >144～<168 | hours | >15～20 | μg/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/Mortality | LC50 | >120～<144 | hours | >10～15 | μg/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/Mortality | LC50 | >144～<168 | hours | >5～10 | μg/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/Mortality | LC50 | >96～<120 | hours | >15～20 | μg/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/Mortality | LC50 | >48～<72 | hours | >15～20 | μg/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/Mortality | LC50 | >144～<168 | 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/Mortality | LC50 | >72～<96 | hours | >10～15 | μg/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/Mortality | LC50 | >96～<120 | hours | 10 | μg/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/Mortality | LC50 | >48～<72 | hours | >20～25 | μg/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/Mortality | LC50 | >36～<48 | hours | >25～30 | μg/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/Mortality | LC50 | >36～<48 | hours | >25～30 | μg/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/Mortality | LC50 | >120～<144 | hours | >5～10 | μg/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/Mortality | NR-ZERO | 25 | days | 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 | Oncorhynchus mykiss | Mortality/Mortality | NR-LETH | >100～<150 | 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/Mortality | LC50 | >48～<72 | hours | >10～15 | μg/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/Mortality | LC50 | >48～<72 | hours | 20 | μg/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/Mortality | LC50 | >144～<168 | hours | >10～15 | μg/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/Mortality | LC50 | >144～<168 | hours | >10～15 | μg/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/Mortality | LC50 | >144～<168 | 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/Mortality | LC50 | >96～<120 | hours | >10～15 | μg/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/Mortality | LC50 | >96～<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/Mortality | LC50 | >144～<168 | hours | >5～10 | μg/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/Mortality | LC50 | >48～<72 | hours | >15～20 | μg/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/Mortality | LC50 | >96～<120 | hours | >20～25 | μg/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/Mortality | LC50 | >36～<48 | hours | >25～30 | μg/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/Mortality | LC50 | >72～<96 | hours | >20～25 | μg/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/Mortality | LC50 | >72～<96 | hours | >10～15 | μg/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/Mortality | LC50 | >120～<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/Mortality | LC50 | >144～<168 | 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/Mortality | LC50 | >168～<200 | 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/Mortality | LC50 | >72～<96 | hours | >15～20 | μg/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/Mortality | LC50 | >168～<200 | 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/Mortality | LC50 | >96～<120 | hours | >15～20 | μg/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/Mortality | LC50 | >96～<120 | hours | >10～15 | μg/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/Mortality | LC50 | >120～<144 | hours | >5～10 | μg/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/Mortality | LC50 | >144～<168 | hours | >20～25 | μg/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/Mortality | LC50 | >144～<168 | hours | >5～10 | μg/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/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | >120～<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/Mortality | LC50 | >144～<168 | hours | >5～10 | μg/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/Mortality | LC50 | >72～<96 | hours | >10～15 | μg/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/Mortality | LC50 | >168～<200 | 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/Mortality | LC50 | >96～<120 | hours | 10 | μg/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/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/Mortality | LC50 | >120～<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/Mortality | LC50 | >48～<72 | hours | >15～20 | μg/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/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/Mortality | LC50 | >48～<72 | hours | >15～20 | μg/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/Mortality | LC50 | >72～<96 | hours | >10～15 | μg/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/Mortality | LC50 | >144～<168 | 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/Mortality | LC50 | >96～<120 | hours | >20～25 | μg/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/Mortality | LC50 | >72～<96 | hours | 10 | μg/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/Mortality | LC50 | >96～<120 | hours | >5～10 | μg/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/Mortality | LC50 | >96～<120 | hours | 10 | μg/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/Mortality | LC50 | >96～<120 | hours | >5～10 | μg/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/Mortality | LC50 | >48～<72 | hours | >20～25 | μg/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/Mortality | LC50 | >144～<168 | hours | >5～10 | μg/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/Mortality | LC50 | >36～<48 | hours | >15～20 | μg/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/Mortality | LC50 | >96～<120 | hours | >20～25 | μg/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/Mortality | LC50 | >120～<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/Mortality | LC50 | >120～<144 | hours | >5～10 | μg/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/Mortality | LC50 | >72～<96 | hours | >10～15 | μg/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/Mortality | LC50 | >48～<72 | hours | >15～20 | μg/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/Mortality | LC50 | >48～<72 | hours | >15～20 | μg/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/Mortality | NR-ZERO | 0.5～24 | 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 | Mortality/Mortality | LC50 | >96～<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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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) | 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 | Mortality/Mortality | LC50 | >36～<48 | hours | >15～20 | μg/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/Mortality | LC50 | >96～<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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/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 | 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 | Mortality/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/Mortality | LC50 | >168～<200 | 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/Mortality | LC50 | >48～<72 | hours | >10～15 | μg/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/Mortality | LC50 | >72～<96 | hours | >15～20 | μg/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/Mortality | LC50 | >120～<144 | hours | >5～10 | μg/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/Mortality | LC50 | >36～<48 | hours | >25～30 | μg/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/Mortality | LC50 | >120～<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/Mortality | LC50 | >144～<168 | hours | >5～10 | μg/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/Mortality | LC50 | >96～<120 | hours | >10～15 | μg/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/Mortality | LC50 | >120～<144 | hours | >10～15 | μg/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/Mortality | LC50 | >144～<168 | 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/Mortality | LC50 | >96～<120 | hours | >5～10 | μg/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/Mortality | NR-LETH | >40～<50 | 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 | 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/Mortality | LC50 | >96～<120 | hours | >15～20 | μg/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/Mortality | LC50 | >120～<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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/Mortality | LC50 | >48～<72 | hours | >10～15 | μg/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/Mortality | LC50 | >96～<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/Mortality | LC50 | >144～<168 | hours | >20～25 | μg/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/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 | 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 | 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/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/Mortality | LC50 | >144～<168 | hours | >15～20 | μg/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/Mortality | LC50 | >72～<96 | hours | >15～20 | μg/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/Mortality | LC50 | >120～<144 | hours | >15～20 | μg/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/Mortality | LC50 | >144～<168 | hours | >15～20 | μg/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/Mortality | LC50 | >36～<48 | hours | >25～30 | μg/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/Mortality | LC50 | >120～<144 | hours | >20～25 | μg/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/Mortality | LC50 | >120～<144 | hours | >15～20 | μg/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/Mortality | LC50 | >120～<144 | hours | >5～10 | μg/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/Mortality | LC50 | >72～<96 | hours | >20～25 | μg/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/Mortality | LC50 | >96～<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/Mortality | LC50 | >48～<72 | hours | 20 | μg/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/Mortality | LC50 | >72～<96 | hours | >10～15 | μg/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/Mortality | LC50 | >144～<168 | hours | >20～25 | μg/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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) | 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/Mortality | LC50 | >72～<96 | hours | >20～25 | μg/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/Mortality | LC50 | >120～<144 | hours | >15～20 | μg/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/Mortality | LC50 | >144～<168 | 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 | 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 | Mortality/Mortality | LC50 | >72～<96 | hours | >5～10 | μg/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/Mortality | LC50 | >120～<144 | hours | >5～10 | μg/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/Mortality | LC50 | >36～<48 | hours | >20～25 | μg/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/Mortality | LC50 | >120～<144 | hours | >20～25 | μg/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/Mortality | LC50 | >48～<72 | hours | >20～25 | μg/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/Mortality | LC50 | >120～<144 | hours | >20～25 | μg/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/Mortality | LC50 | >144～<168 | 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/Mortality | LC50 | >144～<168 | hours | >10～15 | μg/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/Mortality | LC50 | >48～<72 | hours | >15～20 | μg/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/Mortality | LC50 | >120～<144 | hours | >10～15 | μg/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 (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 | 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 | 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 | 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 | 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 | 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 | >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 | >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 | 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 | >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 | 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 | >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 | >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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | >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 | 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 | 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 | >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 | 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 | 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 | 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 | >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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | >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 | >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 | 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 | 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 | 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 | 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 | >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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | μg | 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 | 3.5 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 18 | μg | 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 | 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) | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 18 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | μg | 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 | μg | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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) | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | μg | 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 | >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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 18 | μg | 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 | μg | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | μg | 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 | 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 | >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 | 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) | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | μg | 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 | >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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 42 | days | 90 | μg | 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 | μg | 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 | μg | 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 | >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 | 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 | 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 | >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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 36 | μg | 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 | μg | 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 | μg | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | μg | 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 | 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 | 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 | 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 | 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) | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 56 | days | 36 | μg | 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 | μg | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 36 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | μg | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 14 | days | 90 | μg | 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 | μg | 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) | Growth | NOEC | 70 | days | 90 | μg | 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 | μg | 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 | 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 | 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 | 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 | >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 | 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 | 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) | 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) | 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) | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 70 | days | 90 | μg | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | NOEC | 28 | days | 90 | μg | 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 | μg | 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 | μg | 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 | 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 | 4.5 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 36 | μg | 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 | 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 | 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 | 1.66 | 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 | 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 | 1.21 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | μg | 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 | 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 | >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 | 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 | Carassius auratus (Goldfish) | Accumulation | 50 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 14 | days | 90 | μg | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 28 | days | 36 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | μg | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 42 | days | 90 | μg | 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 | 3.5 | 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) | 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) | 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 | 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 | 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 | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 56 | days | 18 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | Carassius auratus (Goldfish) | Biochemical | LOEC | 70 | days | 18 | μg | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 1.5 | 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 | 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 | >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 | >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 | >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 | >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 | 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 | 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) | 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) | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | >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 | 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 | >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 | 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 | 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 | 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 | >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 | >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 | >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 | >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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | >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 | >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 | 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 | 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 | 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～<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 | 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 | 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 | 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 | 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 | 1.5 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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) | 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) | 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 | 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 | 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 | 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 | 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) | 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) | 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) | 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) | Accumulation | 50 | μg | 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 | μg | 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 | 36 | μg | 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 | 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 | 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 | 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 | 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 | 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) | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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) | 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 | 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) | 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 | 2.38 | 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 | 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 | 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 | 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) | 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 | 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) | 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) | 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) | 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) | 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) | 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) | 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 | 2 | days | 0.000001 | 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 | <0.9～9 | 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) | 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) | 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) | 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) | 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) | 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) | 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) | 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) | 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) | 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) | 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 | 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) | 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) | 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) | 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) | 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) | 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) | 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 | 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) | 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 | 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 | 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 | 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 | 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) | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | >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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | >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～<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 | 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 | 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 | >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 | >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 | 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) | 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) | 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 | 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 | 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 | >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 | 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 | 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 | 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 | >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 | 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 | >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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 9.9 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 2.5 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | >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 | >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 | >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 | >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 | >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 | 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 | >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 | >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 | 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 | 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 | 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 | >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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 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 | 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 | 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 | >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 | 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 | >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 | >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 | >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 | >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 | >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 | >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 | >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 | 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 | >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 | >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 | 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 | 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 | >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 | >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 | >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 | >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 | 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 | 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 | >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 | >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 | >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 | 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 | >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 | 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 | >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 | 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 | 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 | 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) | 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, 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 | EC50 | 85 | days | 0.046 | 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 | NOEC | 38 | days | 0.057 | 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 | 49 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 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 | 78 | days | 0.057 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Nebeker ea 86 | 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 | LOEL | 22 | days | 0.121 | 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 | 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 | 63 | 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 (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) | 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) | 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) | 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 | 45 | days | 0.121 | 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 | 70 | 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 | 56 | days | 0.057 | 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 | 63 | days | 0.016 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Seim ea 84 | 2017/03/01 | |||||||||
| 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 (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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 430 | 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 | 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 | 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 | 151 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 996.3 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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 | 35 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 77 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 253.5 | 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 | >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 | 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 | 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 | 810 | μg/L | meas. (initial) 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 | 47.4 | 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 | 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 | 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 | 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 | 830 | μg/L | meas. (initial) 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 | 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 | 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 | 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 | 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 | 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 | 1959 | 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 | 36.5 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 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 | 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 | 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 | 698 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 1526 | μg/L | meas. (arithm. mean) element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 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 | 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 | 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 | 429 | 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 | 521 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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 | 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 | 12.4 | 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 | 81.1 | μg/L | meas. (arithm. mean) dissolved | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 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 | 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 | 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 | 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 | 600 | μg/L | meas. (initial) dissolved | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 112 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 79.7 | 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 | 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 | μg/L | meas. element | ○ | 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 | 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 | >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 | >200 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | >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 | 892.1 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 289.1 | 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 | publication | 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 | 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 | 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 | 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 | 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 | Pimephales promelas | mortality | LC50 | 96 | hours | 953 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 30.9 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 190.6 | 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 | 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 | 40 | 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 | 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 | 57 | 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 | >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 | 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 | 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 | 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 | 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 | 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 (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 | 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 | 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 | 182.4 | 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 | 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 | 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 | 9.2 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 3 | study report | 2021/10/25 | ||||||
| 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 | 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 | mortality | LC50 | 96 | hours | 226.8 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | mortality | LC50 | 96 | hours | 167.3 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | LC50 | 96 | hours | 42.4 | 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 | >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 | >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 | 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 | 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 | 468.1 | μg/L | meas. (arithm. mean) element | ○ | 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 | 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 | 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 | 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 | 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 | 96 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 172.8 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 (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 | 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 | 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 | 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 (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 | 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 | 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 | 110.9 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 191.7 | 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 (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 | 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 | 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 | 17.2 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 41.1 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 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 | 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 | >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 | 2034 | μg/L | meas. (arithm. mean) element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | >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 | 402.4 | 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 | 11.66 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | The calibrated model is used to calculate LC50 and is evaluated by comparison with published toxicity data sets for freshwater fish (fathead minnow, Pimephales promelas) and Daphnia. | 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 | 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 | 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 | 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 | 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 | 940 | 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 | 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 | 232 | μg/L | meas. 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 | >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 | 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 | 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 | 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 | 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 | 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 | 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 | 15 | μg/L | meas. 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 | 50.1 | 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 | 44.7 | 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 + 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 | 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 | 129 | 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 | 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 | 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 + 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 | 309 | 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 | 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 | 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 | 680 | 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 | 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 | 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 | 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 | 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 | 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 | 114.6 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 490 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 18 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 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 | 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 | 125.7 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 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 | 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 | 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 | 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 | 52 | μg/L | meas. dissolved | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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/Mortality | LC50 | 120 | hours | 84.3 | μg/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 | Lagodon rhomboides | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 36 | hours | 25 | μg/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 | Pimephales promelas | Mortality/Mortality | LC50 | 96 | hours | 84 | μg/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/Mortality | LC50 | 24 | hours | >80～100 | μg/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/Mortality | LC50 | 36 | hours | >60～80 | μg/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 | Intoxication/Immobile | 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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 120 | hours | >15～20 | μg/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 | Clupea harengus | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 108 | hours | >34.9～35.9 | μg/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/Mortality | LC50 | 120 | hours | 53.6 | μg/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/Mortality | LC50 | 72 | hours | >35.9～40 | μg/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/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 | Lepomis macrochirus | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 120 | hours | >10～15 | μg/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 | Lepomis macrochirus | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 84 | hours | 35.9 | μg/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 | Clupea harengus | Mortality/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 | Pimephales promelas | Mortality/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 | Cyprinus carpio | Mortality/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 | Lagodon rhomboides | Mortality/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 | Oncorhynchus mykiss | Mortality/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 | Lagodon rhomboides | Mortality/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 | Oncorhynchus mykiss | Mortality/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 | Pimephales promelas | Mortality/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 | Dicentrarchus labrax | Mortality/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 | Oncorhynchus mykiss | Mortality/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 | Oryzias latipes | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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 | Pimephales promelas | Mortality/Mortality | LC50 | 96 | hours | 530 | μg/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 | Poecilia reticulata | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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 | Oncorhynchus mykiss | Mortality/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 | Pimephales promelas | Mortality/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/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/Mortality | LC50 | 96 | hours | >20～25 | μg/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 | Pimephales promelas | Mortality/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 | Clupea harengus | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 168 | hours | 16.1 | μg/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 | Pimephales promelas | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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/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/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/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/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/Mortality | LC50 | 96 | hours | >15～20 | μg/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 | Lepomis macrochirus | Mortality/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 | Intoxication/Immobile | 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 | Oncorhynchus mykiss | Mortality/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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 | Oryzias latipes | Mortality/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 | Oncorhynchus mykiss | Mortality/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 | Cymatogaster aggregata | Mortality/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 | Intoxication/Immobile | 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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 72 | hours | 15 | μg/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/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/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/Mortality | LC50 | 60 | hours | 60 | μg/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/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/Mortality | LC50 | 96 | hours | 101 | μg/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/Mortality | LC50 | 144 | hours | >5～10 | μg/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/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 | Lepomis macrochirus | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 96 | hours | 3.4 | μg/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/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/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/Mortality | LC50 | 36 | hours | >140～160 | μg/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/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/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 | Pimephales promelas | Intoxication/Immobile | 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 | Cyprinus carpio | Mortality/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/Mortality | LC50 | 120 | hours | >5～10 | μg/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/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/Mortality | LC50 | 48 | hours | >20～25 | μg/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/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/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 | Cyprinus carpio | Mortality/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/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 | Citharichthys stigmaeus | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 96 | hours | 12.7 | μg/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/Mortality | LC50 | 96 | hours | 35.9 | μg/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/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 | Lagodon rhomboides | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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 | Cyprinus carpio | Mortality/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 | Oryzias latipes | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 72 | hours | >10～15 | μg/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/Mortality | LC50 | 168 | hours | 9.2 | μg/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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/Mortality | LC50 | 120 | hours | 83.6 | μg/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/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/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/Mortality | LC50 | 84 | hours | >93～100 | μg/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/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 | Lepomis macrochirus | Mortality/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 | Intoxication/Immobile | 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 | Oncorhynchus mykiss | Mortality/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/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/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/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/Mortality | LC50 | 120 | hours | 81.7 | μg/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/Mortality | LC50 | 36 | hours | 25 | μg/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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/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/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/Mortality | LC50 | 108 | hours | >81.7～93 | μg/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/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 | Clupea harengus | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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/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/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/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/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/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/Mortality | LC50 | 144 | hours | >15～20 | μg/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/Mortality | LC50 | 36 | hours | 30 | μg/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/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/Mortality | LC50 | 24 | hours | >40～60 | μg/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/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/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/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/Mortality | LC50 | 48 | hours | >35.9～40 | μg/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/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/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/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 | Intoxication/Immobile | 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/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/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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 | Oncorhynchus mykiss | Mortality/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/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 | Pimephales promelas | Mortality/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 | Intoxication/Immobile | 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 | Oryzias latipes | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 96 | hours | >5～10 | μg/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/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 | Clupea harengus | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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/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/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/Mortality | LC50 | 48 | hours | >25～30 | μg/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/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 | Oncorhynchus mykiss | Mortality/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/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/Mortality | NR-ZERO | 96 | hours | 190 | μg/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/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/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/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/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/Mortality | LC50 | 48 | hours | >20～25 | μg/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/Mortality | LC50 | 48 | hours | >15～20 | μg/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/Mortality | LC50 | 168 | hours | 21.7 | μg/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/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/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 | Oncorhynchus mykiss | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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 | Pimephales promelas | Intoxication/Immobile | 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 | Oncorhynchus mykiss | Mortality/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 | 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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 84 | hours | >54.4～60 | μg/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/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/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/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/Mortality | LC50 | 96 | hours | 32 | μg/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/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/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 | Cyprinus carpio | Mortality/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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/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 | 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 | 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 | 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 | 640 | μg/L | meas. (initial) dissolved | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss | Mortality/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/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/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 (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 | Mortality/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/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/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/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/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/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/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/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/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/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/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/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 | Cyprinus carpio | Mortality/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/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 | Cyprinus carpio | Mortality/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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/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 | Cyprinus carpio | Mortality/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/Mortality | LC50 | 96 | hours | 308 | μg/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/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/Mortality | NR-ZERO | 96 | hours | 51 | μg/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/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/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/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/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/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/Mortality | LC50 | 36 | hours | 40 | μg/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/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/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/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/Mortality | LC50 | 120 | hours | 54 | μg/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/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/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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/Mortality | LC50 | 48 | hours | 120 | μg/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/Mortality | LC50 | 60 | hours | >100～120 | μg/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/Mortality | LC50 | 72 | hours | 100 | μg/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/Mortality | LC50 | 96 | hours | 93 | μg/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/Mortality | LC50 | 168 | hours | 7.9 | μg/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/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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/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/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/Mortality | LC50 | 108 | hours | >53.6～54.4 | μg/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/Mortality | LC50 | 36 | hours | >20～25 | μg/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/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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 | Pimephales promelas | Mortality/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 | Intoxication/Immobile | 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 | Oncorhynchus mykiss | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/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/Mortality | LC50 | 168 | hours | 11.9 | μg/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 | Pimephales promelas | Intoxication/Immobile | 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 | Pimephales promelas | Intoxication/Immobile | 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 | Oncorhynchus mykiss | Mortality/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/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 120 | hours | 76.6 | μg/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/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/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/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/Mortality | LC50 | 120 | hours | 286 | μg/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/Mortality | LC50 | 120 | hours | 297 | μg/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 | Intoxication/Immobile | 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 | Cyprinus carpio | Mortality/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 | Danio rerio | Mortality/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 | Intoxication/Immobile | 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 | Oncorhynchus mykiss | Mortality/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/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/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/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 | Pimephales promelas | Intoxication/Immobile | 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 | Oncorhynchus mykiss | Mortality/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/Mortality | LC50 | 120 | hours | >20～25 | μg/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 | Clupea harengus | Mortality/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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/Mortality | LC50 | 72 | hours | >15～20 | μg/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/Mortality | LC50 | 72 | hours | 60 | μg/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/Mortality | LC50 | 96 | hours | 8.1 | μg/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 | Pimephales promelas | Mortality/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 | Oncorhynchus mykiss | Mortality/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 | Cyprinus carpio | Mortality/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/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/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 | Lepomis macrochirus | Mortality/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/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/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 | Lepomis macrochirus | Mortality/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/Mortality | LC50 | 96 | hours | 54.4 | μg/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/Mortality | LC50 | 72 | hours | >20～25 | μg/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/Mortality | LC50 | 120 | hours | 34.9 | μg/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/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/Mortality | LC50 | 96 | hours | 10 | μg/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/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/Mortality | LC50 | 120 | hours | 35.1 | μg/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 | Clupea harengus | Mortality/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/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 | Clupea harengus | Mortality/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/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/Mortality | LC50 | 120 | hours | >5～10 | μg/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/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/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/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/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/Mortality | LC50 | 48 | hours | >15～20 | μg/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/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/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 | Oncorhynchus mykiss | Mortality/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/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 | Cymatogaster aggregata | Mortality/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 144 | hours | >20～25 | μg/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/Mortality | LC50 | 96 | hours | 17.2 | μg/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/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 | Cyprinus carpio | Mortality/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/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 | Cyprinus carpio | Mortality/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 | Cyprinus carpio | Mortality/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 | Pimephales promelas | Intoxication/Immobile | 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/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 | Oncorhynchus mykiss | Mortality/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/Mortality | LC50 | 96 | hours | 380 | μg/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/Mortality | LC50 | 72 | hours | >10～15 | μg/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/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/Mortality | LC50 | 12 | hours | 120 | μg/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/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 | Cyprinus carpio | Mortality/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 | Pimephales promelas | Mortality/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 | Oncorhynchus mykiss | Mortality/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/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 | Oryzias latipes | Mortality/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 | Cyprinus carpio | Mortality/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 | Clupea harengus | Mortality/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 | Oncorhynchus mykiss | Mortality/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/Mortality | LC50 | 48 | hours | >60～80 | μg/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/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/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/Mortality | LC50 | 60 | hours | >35.9～40 | μg/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 | Cyprinus carpio | Mortality/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/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 | Oncorhynchus mykiss | Mortality/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 | Clupea harengus | Mortality/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 | Clupea harengus | Mortality/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/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/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/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/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 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 96 | hours | 120 | μg/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/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/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 | Cyprinus carpio | Mortality/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 | Oncorhynchus mykiss | Mortality/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/Mortality | LC50 | 144 | hours | >10～15 | μg/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/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/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/Mortality | LC50 | 144 | hours | >5～10 | μg/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) | 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 | mortality | LC50 | 96 | hours | 23.2 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 980 | μg/L | meas. (initial) 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 | 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 | 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 | 197 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 83.9 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 78.9 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 1000 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 99.6 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 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 | 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 | 155.7 | 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 | 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 | 93 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 62.5 | 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 | 514 | 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 | 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 | 5.9 | 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 | 59.9 | 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 | 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 | 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 | 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 | 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 | 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 | 21.6 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 780 | μg/L | meas. (initial) 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 | 68 | μg/L | meas. dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 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 | 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 | 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 | 653.8 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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 | 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 | 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 | 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 | <=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 | 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 | 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 | 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 | 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 | 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 | 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 | Pimephales promelas | A variety of copper species might be contributing to toxicity and it is evident that toxicity is also affected by water chemistry in ways not related to copper speciation | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | larvae survival | LOEC | 90 | days | 40 | μg/L | Cu | ○ | 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 | 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 | 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 | 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 | 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 (Fathead minnow) | survival and hatch rate and tail movements | NOEC | 2 | days | 338 | μg/L | Cu | ○ | 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 | ○ | 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 | 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 | 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) | 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 | 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) | 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) | biomass | EC10 | 30 | days | 6.1 | μg/L | meas. element | ○ | 12 ECHA Information on Registered Substances | 3 | 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 | 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 | 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 | 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 | 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 | 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 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 | despite significant differences due to NOM source on copper toxicity, DOC and HA concentrations were the most effective parameters in explaining variability in LC50 values | 12 ECHA Information on Registered Substances | 2 | 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 | 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 | 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 | Brachydanio rerio (Zebrafish) | rate and tail movements | 16 | days | Significant mortality of embryos occurred at concentrations of 32 μg Cu/litre and above during the first day of exposure. For exposures of 1-16 μg Cu/litre, hatch was significantly delayed relative to the control value of 4 days and embryo mortality exceeded 50%. Delayed hatching was also reported at concentrations < 1 μg Cu/litre, but effect levels are very uncertain because exposure concentrations were unmeasured and background concentrations are unknown. | 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 | 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 | 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 | 11.9 | μg/L | meas. (arithm. mean) element | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | 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 (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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | Lepomis macrochirus (Bluegill) | Adult bluegill survival and reproduction | LOEC | 22 | months | 162 | μg/L | Cu | ○ | 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) | 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) | 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) | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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) | 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 | 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 | 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) | 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 | |||||
| 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 | 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 | Pimephales promelas (Fathead minnow) | survival and hatch rate and tail movements | LOEC | 2 | days | 621 | μg/L | Cu | ○ | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Fundulus heteroclitus | fish are more senstive in freshwater followed by marine waters and least sensitive in estuarine waters.. | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | pH and hardness influenced copper toxicity | 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) | Regression analysis indicated that only Cu2+and CuOH+could be significantly correlated with growth rate. | 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 | 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 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 | 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 | 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 | 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 | 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) | 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) | 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 | 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 | 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 | 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 | 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 | 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) | 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) | 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 | 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 | 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 | 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 | 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) | 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 | Pimephales promelas (Fathead minnow) | embryos with abnormalities rate and tail movements | LOEC | 2 | days | 338 | μg/L | Cu | ○ | 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) | 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 | Pimephales promelas (Fathead minnow) | LC50 | 28 | days | 128 | μg/L | Cu | ○ | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 (Condition index) | NOEC | 21 | days | 58.83 | μg/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 | Development/Abnormal | NOEC | 21 | days | 58.83 | μg/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/Spawning frequency | NOEC | 21 | days | 58.83 | μg/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/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 | 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 | 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 | Pimephales promelas | Reproduction/Progeny counts/numbers | NOEC | 21 | days | 58.83 | μg/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 | 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 | Reproduction/Size | LOEC | 21 | days | 58.83 | μg/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/Growth, general | 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 | Oncorhynchus mykiss | Mortality/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 | Pimephales promelas | Mortality/Survival | NOEC | 21 | days | 58.83 | μg/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 | ○ | 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 | 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 | Pimephales promelas (Fathead minnow) | survival | LOEC | 28 | days | 113 | μg/L | Cu | ○ | 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 | 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 | 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 | 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) | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 (Fathead minnow) | growth, abnormalities rate and tail movements | LOEC | 28 | days | <=61 | μg/L | Cu | ○ | 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 | 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 | 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 | 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 |