【注意事項】
* 化学物質有害性情報データベース情報更新日が2019年9月以前はRead-acrossデータでも○としていないので、毒性値の取り扱いには注意が必要である。
| 生物種 | 学名 | 影響内容 | エンドポイント | 暴露期間(値) | 暴露期間(単位) | 毒性値 | 毒性値(単位) | Read-across * | QSAR | GLP | 設定濃度 | 実測濃度 | 情報源 | 情報源による信頼性評価 | 著者 | タイトル | 記載誌 | 発行年 | 情報更新日 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| subject type | scientific name | effect | endpoint | exposure duration value | exposure duration unit | toxicity value | toxicity unit | Read-across | QSAR | GLP | nominal concentration | measured concentration | original work type | original work reliability rank | author | title | referenced journal | publication year | Information update date |
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass, the growth rate, the pigment diversity , the autotrophic index | an optimal concentration range | 1～35 | μg/L [Cu] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 3 | days | 10 | mg/L [~10 mg/L, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Fungi | Reproduction (Seed or spore production) | LOEC | 21 | days | 100 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pradhan,A., S. Seena, C. Pascoal, and F. Cassio | Can Metal Nanoparticles be a Threat to Microbial Decomposers of Plant Litter in Streams? | Microb. Ecol.62(1): 58-68 | 2011 | 2019/02/13 | ||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 8 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LT50 | 0.83 | days | 100 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | 3 | days | 0.504 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | EC50 | 3 | days | 0.014 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | EC50 | 3 | days | 11.55 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | EC50 | 3 | days | 0.71 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | EC50 | 3 | days | 0.025 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Fungi | Population (Biomass) | LOEC | 21 | days | 100 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pradhan,A., S. Seena, C. Pascoal, and F. Cassio | Can Metal Nanoparticles be a Threat to Microbial Decomposers of Plant Litter in Streams? | Microb. Ecol.62(1): 58-68 | 2011 | 2019/02/13 | ||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 2 | days | 40 | mg/L [~40 mg/L, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 2.5 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 5 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 7 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | 3 | days | 9.1 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 1.5 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 4 | days | 2.8 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | Chlorella sp. | Physiology (Photosystem II (PSII) electron transport activity) | IC50 | 0.02 | days | 47 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 藻類 | Chlorella sp. | Physiology (Photosystem II (PSII) electron transport activity) | IC50 | 0.02 | days | 57 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | EC50 | 3 | days | 0.02 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | 30 | mg/L [~30 mg/L, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 8 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 4 | days | 4.3 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 3 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 2.5 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 2 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 5 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | 7 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | |||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | others Nitellopsis obtusa | Mortality | LC50 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | EC20 | 72 | hours | 0.504 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | EC20 | 72 | hours | 9.1 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | NOEC | 3 | days | 6.4 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | EC50 | 3 | days | 0.025 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | NOEC | 3 | days | 8.03 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | NOEC | 3 | days | 0.421 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth (Growth rate) | NOEC | 3 | days | 6.4 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | EC50 | 3 | days | 25 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | NOEC | 3 | days | 6400 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | NOEC | 3 | days | 6400 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | NOEC | 3 | days | 8030 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | NOEC | 3 | days | 421 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Chlorella sp. Chlorella sp. | Physiology | IC50 | 0.5 | hours | 47000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thomas | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2018/03/16 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | EC50 | 3 | days | 25 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | EC50 | 3 | days | 710 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Chlorella sp. Chlorella sp. | Physiology | IC50 | 0.5 | hours | 57000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thomas | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2018/03/16 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | EC50 | 3 | days | 14 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | EC50 | 3 | days | 11550 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | EC50 | 3 | days | 20 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2018/03/09 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | EC20 | 3 | days | 9100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth | EC20 | 3 | days | 504 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2016/03/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | EC50 | 72 | hours | 0.025 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | EC50 | 72 | hours | 11.55 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | EC50 | 72 | hours | 0.02 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | EC50 | 72 | hours | 0.71 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | EC50 | 72 | hours | 0.014 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | EC50 | 72 | hours | 0.025 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 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 | publication | 2021/10/25 | |||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 18 | μg/L [meas. (initial) element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | growth rate | EC50 | 72 | hours | 46 | μg/L [meas. (initial) element] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 824 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 245 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 122 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 32 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 194 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 36.9 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 163 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 84 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 152 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 602 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 92 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 368 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 811 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 199 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 462 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 219 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 16.5 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 190 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 156 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 268 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 35 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 93 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 346 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 111 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 773 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 99 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 209 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 506 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 296 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 254 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 60 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 200 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 446 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 238 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 987 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 35 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 380 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 59 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 205 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 174 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 55 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 105 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 99 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 151 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 30 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 51 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 440 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 108 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 52.7 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 65.4 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 33.9 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 230 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 113 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 178 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 281 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 161 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 685 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 102 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 97.4 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 208 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 100 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 333 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 193 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 756 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/03/08 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 364 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/03/08 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | NOEC | 72 | hours | 0.421 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | NOEC | 72 | hours | 8.03 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | NOEC | 72 | hours | 6.4 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Raphidocelis subcapitata | Growth rate | NOEC | 72 | hours | 6.4 | mg/L | 16 ECOTOX | Aruoja,V., H.C. Dubourguier, K. Kasemets, and A. Kahru | Toxicity of Nanoparticles of CuO, ZnO and TiO2 to Microalgae Pseudokirchneriella subcapitata | Sci. Total Environ.407(4): 1461-1468 | 2009 | 2022/01/25 | ||||||
| 藻類 | Chlorella vulgaris | NOEC/L(E)C10 | 137 | その他others [μg Cu/L] | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
| 藻類 | Phaeodactylum tricornutum | NOECs/EC10 | 4 | μg/L | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
| 藻類 | Chlorella vulgaris | NOEC(s) / EC10 | 137 | その他others [μgCu/L] | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
| 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 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 56.4 | 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 | 61.8 | 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 | 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 | 49 | 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 | 49 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 23.1 | μg/L [meas. dissolved] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | |||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 164 | μg/L [meas. dissolved] | 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 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 35.4 | 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 | 19.3 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.A.C. & Janssen, C.R. | A biotic ligand model predicting acute copper toxicity to Daphnia magna: the effects of calcium, magnesium, sodium, potassium and pH | Environ.Sci.Technol. 36, 48-84 | 2021/10/25 | ||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 15.7 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 13.5 | μg/L [meas. (initial) 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 | |||||
| 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 | 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) | biomass | NOEC | 72 | hours | 15.7 | μg/L [meas. (initial) 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 | |||||
| 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 | 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) | biomass | NOEC | 72 | hours | 17.9 | μg/L [meas. (initial) 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 | |||||
| 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 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 23.1 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.A.C et al. | Refinement and field validation of a biotic ligand model predicting acute copper toxicity to Daphnia magna | Comparative biochemistry and physiology part C, 133, 243-258 | 2021/10/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 61.8 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 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 | 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 | 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 | Vardy DW, Oellers J, Doering JA, Hollert H, Giesy JP, Hecker M | Sensitivity of early life stages of white sturgeon, rainbow trout and fathead minnow to copper | Ecotoxicology 22:139-147 | 2021/10/25 | |||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 23.1 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | 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 | 65.5 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 61.8 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) | biomass | NOEC | 72 | hours | 52.9 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | publication | 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 | publication | 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 | publication | 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 | 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 | 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 | 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 | study report | 2021/10/25 | ||||||||
| 藻類 | other algae: Raphidocelis subcapitata | biomass | NOEC | 72 | hours | 35.4 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 藻類 | 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 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 188 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 188 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 31 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 510 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 56 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Phaeodactylum tricornutum | growth rate | EC10 | 72 | hours | 2.9 | μg/L [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 | 2003 | 2018/02/17 | |||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 57.5 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 36 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 407 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 111.2 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 112.8 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 59.1 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 110.6 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 63.9 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Skeletonema costatum | growth rate | NOEC | 72 | hours | 7.54 | μg/L [dissolved] | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/02/17 | ||||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 108 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 159 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 89.2 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 132 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 84 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Phaeodactylum tricornutum | growth rate | NOEC | 72 | hours | 5.7 | μg/L [dissolved] | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/03/08 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 37.6 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 173 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 99 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 85 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 162 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 49.4 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 283 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 53.3 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 404 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol | 2006 | 2018/03/08 | |||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 91.3 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 54.6 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 60.2 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 97.2 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 170.8 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 67.7 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 53.7 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 174 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 19.4 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 40.8 | μg/L [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 | 2003 | 2018/02/18 | ||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | NOEC | 2 | days | 0.4 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 874 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | NOEC | 2 | days | 40 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 152 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 92.7 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 546 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 90.3 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 1550 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 112 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | LC50 | 2 | days | 2.6 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 1518 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 217 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 129 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 1054 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | NOEC | 1 | days | 20 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | >1500 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | EC50 | 1 | days | 593 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 1566 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 149 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 200 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | >200 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | LC50 | 2 | days | 131.8 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | NOEC | 1 | days | 0.4 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 1737 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | LC50 | 1 | days | 8.5 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | LC50 | 1 | days | 75.6 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | LC50 | 1 | days | 1.7 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | LC50 | 1 | days | 9.8 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | 1 | days | 1.32 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | |||||||
| 甲殻類 | others Thamnocephalus platyurus | Mortality | 1 | days | 49.7 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | |||||||
| 甲殻類 | others Tigriopus japonicus | Mortality | 4 | days | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Park,J., S. Kim, J. Yoo, J.S. Lee, J.W. Park, and J. Jung | Effect of Salinity on Acute Copper and Zinc Toxicity to Tigriopus japonicus: The Difference Between Metal Ions and Nanoparticles | Mar. Pollut. Bull.85(2): 526-531 | 2014 | 2019/02/13 | ||||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 799 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | 2 | days | 90.7 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | |||||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | 2 | days | 0.96 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2019/02/13 | |||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 844 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | EC50 | 2 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lewis,M.A. | Effect of Loading Density on the Acute Toxicities of Surfactants, Copper, and Phenol to Daphnia magna Straus | Arch. Environ. Contam. Toxicol.12(1): 51-55 | 1983 | 2019/02/13 | |||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 224 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | >1500 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 160 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 92.7 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 844000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Intoxication | NOEC | 2 | days | 400 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | >1500000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Intoxication | NOEC | 2 | days | 40000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Intoxication | LC50 | 2 | days | 131800 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Intoxication | LC50 | 2 | days | 2600 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 200000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Intoxication | EC50 | 2 | days | 11～39 | [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lewis,M.A. | Effect of Loading Density on the Acute Toxicities of Surfactants, Copper, and Phenol to Daphnia magna Straus | Arch. Environ. Contam. Toxicol.12(1): 51-55 | 1983 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 149000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 1566000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 799000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | >1500000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 160000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 224000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | >200000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 92700 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 1737000 | μg/L [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia magna | Physiology | LC20 | 2 | days | 90700 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | LC20 | 2 | days | 960 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 1737 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 0.4 | mg/L | 16 ECOTOX | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 40 | mg/L | 16 ECOTOX | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | LC50 | 48 | hours | 131.8 | mg/L | 16 ECOTOX | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | LC50 | 48 | hours | 2.6 | mg/L | 16 ECOTOX | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | LC20 | 48 | hours | 90.7 | mg/L | 16 ECOTOX | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | LC20 | 48 | hours | 0.96 | mg/L | 16 ECOTOX | Heinlaan,M., A. Ivask, I. Blinova, H.C. Dubourguier, and A. Kahru | Toxicity of Nanosized and Bulk ZnO, CuO and TiO2 to Bacteria Vibrio fischeri and Crustaceans Daphnia magna and Thamnocephalus platyurus | Chemosphere71(7): 1308-1316 | 2008 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 149 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 200 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 1566 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 1500 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 160 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 11～39 | μg/L | 16 ECOTOX | Lewis,M.A. | Effect of Loading Density on the Acute Toxicities of Surfactants, Copper, and Phenol to Daphnia magna Straus | Arch. Environ. Contam. Toxicol.12(1): 51-55 | 1983 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 200 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 844 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 224 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 92.7 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 1500 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | EC50 | 48 | hours | 799 | mg/L | 16 ECOTOX | Blinova,I., A. Ivask, M. Heinlaan, M. Mortimer, and A. Kahru | Ecotoxicity of Nanoparticles of CuO and ZnO in Natural Water | Environ. Pollut.158(1): 41-47 | 2010 | 2022/01/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | L(E)C50 | 34 | その他others [μgCu/L] | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 79.2 | 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 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 29.8 | 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 | 68.31 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 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 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 10.4 | 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 | 134.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 322 | 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 | 9.2 | 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 | 292 | 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 | 332 | 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 | 53.8 | 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 | 311 | 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 | 542 | 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 | 14.74 | 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 | 2.8 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 7.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | 50.6 | 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 | 220 | 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 | 128 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 304 | 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 | 192 | 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 | 86.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 638 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | publication | 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 | publication | 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 | publication | 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 | 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 | 31.65 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 279 | 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 | 30 | μg/L [meas. 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 | 42 | μg/L [meas. (initial) 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 | 39 | μg/L [meas. (initial) 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 | 44 | 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 | 14 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 87 | 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 | LC50 | 48 | hours | 4.8 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 69 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | 124 | 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 | LC50 | 48 | hours | 22.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 15.3 | 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 | 16.7 | 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 | 21.1 | 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 | immobility | EC50 | 48 | hours | 71 | 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 | LC50 | 48 | hours | 159 | 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 | 25.2 | 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 | immobility | EC50 | 48 | hours | 93 | 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 | 9 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 99 | 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 | 25.3 | 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 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 12 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 47.3 | 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 | 130.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 122.5 | 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 | 88.8 | 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 | 100 | 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 | 178 | μg/L [meas. 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 | 23 | μg/L [meas. (initial) 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 | 109.7 | 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 | 78.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 60.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 104 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 100 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 14.5 | 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 | 77.3 | μg/L [meas. 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 | 25 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 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 | mortality | EC50 | 48 | hours | 118.5 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 101.8 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | 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 | μg/L [meas. 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 | 31 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 39 | μg/L [meas. 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 | 177 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 157 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30.8 | 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 | 38.2 | 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 | 45.1 | 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 | Daphnia magna | mortality | LC50 | 48 | hours | 187.6 | 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 | 35.23 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 34.4 | μg/L [meas. 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 | mortality | EC50 | 48 | hours | 43.1 | 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 | Daphnia magna | mortality | LC50 | 48 | hours | 2 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 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 | 11 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 24 | hours | 23.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Markich SJ, Batley GE, Stauber JL, Rogers NJ, Apte SC, Hyne RV, Bowles KC, Wilde KL, Creighton NM | Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota | Chemosphere 60:1-8 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 47 | μg/L [meas. 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 | 30 | μg/L [meas. (initial) 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 | 6.5 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 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 | 11.4 | μg/L [meas. 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 | 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 | 77.4 | 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 | LC50 | 48 | hours | 11.1 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 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 | 10 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 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 | 106.4 | 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 | Daphnia magna | immobility | EC50 | 48 | hours | 109 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 40 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 34 | 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 | 135.5 | 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 | 7.4 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 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 | 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 | 87.39 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 116.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 11.3 | 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 | 3.98 | 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 | 6.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 19.28 | 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 | 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 | 96.23 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | <13 | 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 | mobility | EC50 | 48 | hours | 14 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | <5 | 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 | 19.24 | 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 | 6.18 | 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 | 28.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | 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 | 8.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 24.43 | 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 | 50 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | 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 | 5.5 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 155.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 32 | μg/L [meas. (initial) 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 | 15.58 | 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 | 6.03 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 10.14 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 37.78 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 1.6 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 4.9 | 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 | Daphnia magna | immobility | EC50 | 48 | hours | 207 | 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 | 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 | 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 | Daphnia magna | mobility | EC50 | 96 | hours | 5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 96 | hours | 42 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 314 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Long KE, Van Genderen EJ, Klaine SJ | The effects of low hardness and pH on copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(1):72-75 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 6.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | 308 | 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 | 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 | mobility | EC50 | 48 | hours | 50 | 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 | 9.46 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Hyne RV, Pablo F, Julli M, Markich SJ | Influence of water chemistry on the acute toxicity of copper and zinc to the cladoceran Ceriodaphnia cf dubia | Environmental Toxicology and Chemistry 24(7);1667-1675 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 24 | hours | 12 | 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 | 9.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 151 | 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 | immobility | EC50 | 48 | hours | 276 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | immobility | EC50 | 48 | hours | 430 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | immobility | EC50 | 48 | hours | 6.5 | μg/L [meas. (initial) 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 | immobility | EC50 | 48 | hours | 1.6 | μg/L [meas. (initial) 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 | immobility | EC50 | 48 | hours | 2.2 | μg/L [meas. (initial) 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 | immobility | EC50 | 48 | hours | 73 | μg/L [meas. (initial) 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 | immobility | EC50 | 48 | hours | 1.6 | μg/L [meas. (initial) 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 | mobility | EC50 | 48 | hours | 9.7 | 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 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 6.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 170 | μg/L [meas. 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 | 2.8 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 208 | μg/L [meas. 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 | 16 | μg/L [meas. (initial) 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 | immobility | EC50 | 48 | hours | 11 | μg/L [meas. (initial) 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 | immobility | EC50 | 48 | hours | 23 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | immobility | EC50 | 48 | hours | 42 | μg/L [meas. (initial) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 21 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | 40.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 18 | 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 | 81.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Kramer KJM, Jak RG, Van Hattum B, Hooftman RN, Zwolsman JJG | Copper toxicity in relation to surface water-dissolved organic matter: biological effects to Daphnia magna | Environmental Toxicology and Chemistry 23(12):2971-2980 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 275 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 607 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 60.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 212 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Vasconcelos FM, Tack FMG, Allen HE, Janssen CR | Effect of dissolved organic matter source on acute copper toxicity to Daphnia magna | Environmental Toxicology and Chemistry 23(5):1248-1255 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 372 | 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 | 24.8 | 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 | 21.6 | μg/L [meas. (arithm. mean) 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 | EC50 | 48 | hours | >184.7 | 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 | mobility | EC50 | 48 | hours | 14.7 | μg/L [meas. (arithm. mean) 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 | 19.4 | μg/L [meas. (arithm. mean) 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 | 108.8 | 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 | 32 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 257 | 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 | 7.8 | 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 | 32.3 | 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 | mobility | EC50 | 48 | hours | 29.4 | 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 | 17.8 | 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 | 68.4 | μg/L [meas. (arithm. mean) 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 | EC50 | 48 | hours | 48.2 | 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 | 4.3 | μg/L [meas. (arithm. mean) 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 | 25.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere KAC, Bossuyt BTA, Janssen CR | Variability of the protective effect of sodium on the acute toxicity of copper to freshwater cladocerans | Environmental Toxicology and Chemistry 26(3):535-542 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | 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 | 24.3 | 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 | 56.9 | 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 | 59.9 | 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 | 12.1 | 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 | Daphnia magna | mobility | EC50 | 48 | hours | 2.5 | 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 | EC50 | 48 | hours | 157 | 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 | 53.2 | μg/L [meas. 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 | 125.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 206 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | 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 | 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 | 60 | 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 | mortality | EC50 | 48 | hours | >111 | 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 | 156.1 | 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 | mortality | EC50 | 48 | hours | 147 | 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 | mortality | EC50 | 48 | hours | 267 | 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 | mortality | EC50 | 48 | hours | 30 | 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 | 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 | mortality | LC50 | 48 | hours | 12 | 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 | mortality | LC50 | 48 | hours | 2 | μg/L [meas. (arithm. mean) Total Cu] | ○ | 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 | 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 | 6.2 | 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 | 67.3 | μg/L [meas. (arithm. mean) 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 | EC50 | 48 | hours | 8.3 | 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 | 12.1 | 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 | 27.8 | 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 | 5.7 | 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 | 100 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 7.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 66.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 3.7 | 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 | 8.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 30.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 56.1 | 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 | 72 | 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 | 104.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Villavicencio G, Urrestarazu P, Carvajal C, De Schamphelaere KAC, Janssen CJ, Torres JC, Rodriguez PH | Biotic Ligand Model prediction of copper toxicity to daphnids in a range of natural waters in Chile | Environmental Toxicology and Chemistry 24(5):1287-1299 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 8.9 | 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 | Daphnia magna | mortality | LC50 | 48 | hours | 1.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 8.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | 26.6 | 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 | immobility | EC50 | 48 | hours | 29.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 7 | 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 | 17.7 | 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 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 9.3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 8.3 | 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 | 5.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 18.8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 0.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 81.06 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 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 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 42.2 | 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 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 7.3 | 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 | Daphnia magna | immobility | EC50 | 48 | hours | 7.4 | 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 | 16.5 | 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 | 14.1 | 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 | 2.6 | μg/L [meas. 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 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 58.5 | 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 | mortality | LC50 | 48 | hours | 78.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 61.82 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Fulton BA, Meyer JS | Development of a regression model to predict copper toxicity to Daphnia magna and site-specific copper criteria across multiple surface-water drainages in an arid landscape | Environmental Toxicology and Chemistry 33(8):1865-1873 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 302 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 23.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | 4.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 25.9 | 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 | 148 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Genderen E, Gensemer R, Smith C, Santore R, Ryan A | Evaluation of the Biotic Ligand Model relative to other site-specific criteria derivation methods for copper in surface waters with elevated hardness | Aquatic Toxicology 84:279-291 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 26.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 29.3 | 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 | 20.3 | 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 | 44.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 37 | 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 | 36.3 | 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 | 5.02 | 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 | 5.38 | 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 | 39.5 | 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 | mortality | LC50 | 48 | hours | 207 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 10.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Tomasso JR, Klaine SJ | Influence of pH, hardness, dissolved organic carbon concentration, and dissolved organic matter source on the acute toxicity of copper to Daphnia magna in soft waters: implications for the Biotic Ligand Model | Environmental Toxicology and Chemistry 28(8):1663-1670 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 131 | 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 | EC50 | 48 | hours | 26 | μg/L | 10 EHC (Environmental Health Criteria) | Lewis MA | Effect of loading density on the acute toxicities of surfactants, copper, and phenol to Daphnia magna Straus | Arch Environ Contam Toxicol,12 Environ Contam Toxicol, 12 | 2022/01/20 | ||||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 9.8 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | 2018/03/08 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 76 | μg/L [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 | 1990 | 2018/03/08 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 91 | μg/L [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 | 1990 | 2018/03/08 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 84 | μg/L [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 | 1990 | 2018/03/08 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 31 | μg/L [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 | 1990 | 2018/03/08 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 366 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 188 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/07 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 10.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/07 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 8.5 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/07 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 332 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 70 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 60 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 295 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 399 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 40 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 33.8 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 37.9 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 529 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 90 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 92.6 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 648 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 257 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 484 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 119 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 826 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 93 | μg/L [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 | 1990 | 2018/03/08 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 526 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 686 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 210 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 281 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 292 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 106 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 200 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 35.2 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31.8 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 40.9 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 152 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 10 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 35 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 175 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 58 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 7 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 792 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 56 | μg/L [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 | 1990 | 2018/03/08 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2018/03/07 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2018/03/07 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L [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 | 1990 | 2018/03/08 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 52 | μg/L [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 | 1990 | 2018/03/08 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 14 | μg/L [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 | 1990 | 2018/03/08 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 388 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 50 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 157 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 9.5 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/07 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 300 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 44 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 136 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 229 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/07 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 244 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 66 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 421 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 43 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 69 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2018/03/07 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 289 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 117 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 109 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/07 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/07 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 465 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2018/03/07 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 1213 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/03/08 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 36 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 25 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 23 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 32 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 33 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 34 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 51 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 27 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/07 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 200 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/07 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 20 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 22 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 42 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/03/08 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 380 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 798 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 63 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/17 | ||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 48.3 | ppm | 3 USEPA Pesticide Ecotoxicity Database | J. Sylvester | 1997 | 2018/02/20 | |||||||||
| 甲殻類 | others Penaeus monodon | NOECs/EC10 | 145 | μg/L | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
| 甲殻類 | others Ceriodaphnia dubia and Oncorhynchus mykiss | NOEC(s) / EC10 | 12 | その他others [μgCu/L] | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 118 | 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 | reproduction | NOEC | 21 | days | 71.4 | 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 | reproduction | EC50 | 21 | days | 10.3 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 32.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 6 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 10.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 73.6 | 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 | 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 | EC20 | 21 | days | 47 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | 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 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 | 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 | 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 | 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 | EC10 | 21 | days | 70.5 | 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 | 133 | 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 | |||||
| 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 | Ceriodaphnia dubia | reproduction | EC10 | 7 | days | 46 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | study report | 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 | 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 | 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 | |||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 181 | 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 | 56.2 | 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 | 21.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 46.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | 76.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Van Regenmortel T, Janssen CR, De Schamphelaere KAC | Comparison of the capacity of two biotic ligand models to predict chronic copper toxicity to two Daphnia magna clones and formulation of a generalized bioavailability model | Environmental Toxicology and Chemistry 34(7): 1597-1608 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 83.9 | μg/L [meas. element] | ○ | 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 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 14.4 | μg/L [meas. element] | ○ | 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 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 41.7 | μg/L [meas. element] | ○ | 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 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC20 | 21 | days | 62.1 | 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 | 79.6 | 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 | 12 | 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 | EC20 | 21 | days | 36.1 | 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 | EC10 | 21 | days | 55.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 50.2 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | 18 | 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 | mortality | NOEC | 42 | days | 20 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 40 | μg/L [dissolved] | 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 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 22 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 20 | μg/L | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 10 | μg/L | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | EC10 | 7 | days | 29 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 10 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | ||||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | EC10 | 7 | days | 34 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | LOEC | 21 | days | 30 | 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 | 56.1 | 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 | 57.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4):449-455 | 2021/10/25 | |||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 8 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | EC10 | 7 | days | 25 | 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 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC10 | 7 | days | 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 | |||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L [dissolved] | 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 | 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 | 5.7 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | 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 | NOEC | 21 | days | 36.8 | μg/L [meas. dissolved] | 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 | growth | NOEC | 21 | days | 12.6 | μg/L [meas. dissolved] | 12 ECHA Information on Registered Substances | 2 | Wang N, Mebane CA, Kunz JL, Ingersoll CG, Brumbaugh WG, Santore RC, Gorsuch JW, Arnold WR | Influence of dissolved organic carbon on toxicity of copper to a unionid mussel (Villosa iris) and a cladoceran (Ceriodaphnia dubia) in acute and chronic water exposures | Environmental Toxicology and Chemistry 30(9):2115-2125 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 34.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Adam N, Vakurov A, Knapen D, Blust R | The chronic toxicity of CuO nanoparticles and copper salt to Daphnia magna | Journal of Hazardous materials 283:416-422 | 2021/10/25 | |||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 28 | 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 | |||||
| 甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 4 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Van Regenmortel T, Janssen CR, De Schamphelaere KAC | Comparison of the capacity of two biotic ligand models to predict chronic copper toxicity to two Daphnia magna clones and formulation of a generalized bioavailability model | Environmental Toxicology and Chemistry 34(7): 1597-1608 | 2021/10/25 | ||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 29 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 17 | 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 | 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 | 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 | 91 | 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 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC10 | 7 | days | 65 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC10 | 7 | days | 10 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 甲殻類 | Ceriodaphnia dubia | mortality | EC10 | 7 | days | 20 | 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 | 5.9 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 32.8 | 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 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 75.6 | 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 pulex | mortality | NOEC | 42 | days | 15 | μg/L [dissolved] | 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 | 30 | μg/L [dissolved] | 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 | 5 | μg/L [dissolved] | 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 | 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 | 68.8 | 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 sp. | reproduction | NOEC | 7 | days | 20 | μg/L [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. | 1990 | 2018/02/17 | |||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 20 | μg/L [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. | 1990 | 2018/02/17 | |||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 31.6 | μg/L [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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 181 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | |||||||
| 甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 19 | μg/L | 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. | 1995 | 2018/03/09 | |||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 24.1 | μg/L [dissolved] | 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. | 1989 | 2018/02/17 | |||||
| 甲殻類 | Mercenaria mercenaria | development | NOEC | 288 | hours | 7 | μg/L | 12 ECHA Information on Registered Substances | 2 | LaBreche, T.M.C. et al. | Copper Toxicity to Larval Mercenaria mercenaria (hard clam) | Environ Toxicol Chem | 2002 | 2018/03/09 | |||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 20 | μg/L [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. | 1990 | 2018/02/17 | |||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 10 | μg/L | 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. | 1995 | 2018/03/09 | |||||
| 甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 19.53 | μg/L [Total + labile Cu] | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/03/09 | ||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 10 | μg/L [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. | 1990 | 2018/02/17 | |||||
| 甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 10.42 | μg/L [Total + labile Cu] | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/03/09 | ||||||
| 甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 122 | μg/L [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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 6.3 | μg/L [dissolved] | 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. | 1989 | 2018/02/17 | |||||
| 甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 12.83 | μg/L [Total + labile Cu] | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/03/09 | ||||||
| 甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 4 | μg/L | 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. | 1995 | 2018/03/09 | |||||
| 甲殻類 | Mytilus edulis | Embryo development | NOEC | 48 | hours | 6.2 | μg/L [Total dissolved + labile Cu] | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/03/09 | ||||||
| 甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 4 | μg/L | 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. | 1995 | 2018/03/09 | |||||
| 甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 10.89 | μg/L [Total + labile Cu] | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/03/20 | ||||||
| 甲殻類 | Dendraster excentricus | embryo development | EC50 | 48 | hours | >75.8 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Neanthes arenaceodentata | growth | NOEC | 28 | days | 13.5 | μg/L | × | 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. 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. | 1986 | 2018/03/09 | ||||
| 甲殻類 | Strongylocentrotus purpuratus | embryo development | EC50 | 72 | hours | 24.3 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 30 | μg/L [dissolved] | 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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L [dissolved] | 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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 106 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 68.8 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 71.4 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 21.5 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 28 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | |||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L [dissolved] | 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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Neanthes arenaceodentata | growth | NOEC | 28 | days | 12.1 | μg/L | × | 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. 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. | 1986 | 2018/03/09 | ||||
| 甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 40 | μg/L [dissolved] | 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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Ceriodaphnia dubia | mortality | NOEC | 7 | days | 20 | μg/L | 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 | 1993 | 2018/02/17 | |||||
| 甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 10 | μg/L | 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 | 1993 | 2018/02/17 | |||||
| 甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 47.13 | μg/L [Total + labile Cu] | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/03/09 | ||||||
| 甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 28.19 | μg/L [Total + labile Cu] | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/03/09 | ||||||
| 甲殻類 | Tisbe battagliai | mortality | NOEC | 21 | days | 18 | μg/L [dissolved] | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/03/09 | ||||||
| 甲殻類 | Tisbe battagliai | reproduction | NOEC | 21 | days | 18 | μg/L [dissolved] | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/03/09 | ||||||
| 甲殻類 | Tisbe battagliai | development | NOEC | 21 | days | 18 | μg/L [dissolved] | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/03/09 | ||||||
| 甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 4 | μg/L [dissolved] | 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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Chironomus riparius | growth | NOEC | 10 | days | 16.9 | μg/L | 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 | 1991 | 2018/03/09 | |||||
| 甲殻類 | Crassostrea virginica | embryo development | EC50 | 48 | hours | 30.7 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Strongylocentrotus purpuratus | embryo development | EC50 | 72 | hours | 46.4 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Strongylocentrotus purpuratus | embryo development | EC50 | 72 | hours | 30.2 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Strongylocentrotus purpuratus | embryo development | EC50 | 72 | hours | 14.8 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Dendraster excentricus | embryo development | EC50 | 48 | hours | 46.2 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Dendraster excentricus | embryo development | EC50 | 48 | hours | 36.4 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 5 | μg/L [dissolved] | 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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Crassostrea virginica | embryo development | EC50 | 48 | hours | 40.7 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Crassostrea virginica | embryo development | EC50 | 48 | hours | 22.4 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Crassostrea virginica | embryo development | EC50 | 48 | hours | 11.2 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 21.6～25.2 | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | A comparison of the copper sensitivity of two economically important saltwater mussel species and a review of previously reported copper toxicity data for mussels: important implications for determining future ambient copper saltwater criteria for the USA | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2018/03/09 | |||||
| 甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 14～17.5 | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | A comparison of the copper sensitivity of two economically important saltwater mussel species and a review of previously reported copper toxicity data for mussels: important implications for determining future ambient copper saltwater criteria for the USA | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2018/03/09 | |||||
| 甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 8.03～9.9 | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | A comparison of the copper sensitivity of two economically important saltwater mussel species and a review of previously reported copper toxicity data for mussels: important implications for determining future ambient copper saltwater criteria for the USA | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2018/03/09 | |||||
| 甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 3.52～4.66 | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | A comparison of the copper sensitivity of two economically important saltwater mussel species and a review of previously reported copper toxicity data for mussels: important implications for determining future ambient copper saltwater criteria for the USA | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2018/03/09 | |||||
| 甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L [dissolved] | 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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 15 | μg/L [dissolved] | 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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 10 | μg/L [dissolved] | 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 | 1985 | 2018/03/09 | |||||
| 甲殻類 | Dendraster excentricus | embryo development | EC50 | 48 | hours | 18.9 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem | 2010 | 2018/03/09 | |||||
| 甲殻類 | Daphnia magna | NOEL | 48 | hours | 13 | ppm | 3 USEPA Pesticide Ecotoxicity Database | J. Sylvester | 1997 | 2018/02/28 | |||||||||
| 魚類 | Oncorhynchus mykiss | Growth (Specific growth rate) | NOEC | 4 | weeks | 411.9 | μg/g | 16 ECOTOX | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2022/01/25 | ||||||
| 魚類 | Cyprinus carpio | Growth (Weight gain) | NOEC | 30 | days | 12.8 | μg/L | 0 ug/L / 12.80 ug/L | 16 ECOTOX | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2022/01/25 | |||||
| 魚類 | Cyprinus carpio | Growth (Length) | NOEC | 30 | days | 12.8 | μg/L | 0 ug/L / 12.80 ug/L | 16 ECOTOX | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2022/01/25 | |||||
| 魚類 | Cyprinus carpio | Growth (Weight gain) | LOEC | 30 | days | 14.65 | μg/L | 0 ug/L / 14.65 ug/L | 16 ECOTOX | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2022/01/25 | |||||
| 魚類 | Cyprinus carpio | Growth (Length) | LOEC | 30 | days | 14.65 | μg/L | 0 ug/L / 14.65 ug/L | 16 ECOTOX | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2022/01/25 | |||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | LOEC | 10 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Accumulation (Residue) | LOEC | 15 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Hediste diversicolor | Feeding behavior (Food consumption) | NOEC | 7 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Hediste diversicolor | Behavior (Burrowing behavior, burrowing length) | NOEC | 4 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Glutathione peroxidase) | LOEC | 7 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Catalase) | LOEC | 3 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Superoxide dismutase (SOD) enzyme activity) | LOEC | 3 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Growth (Length) | LOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.2266 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Accumulation (Residue) | LOEC | 7 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Hediste diversicolor | Enzyme(s) (Glutathione S-transferase) | LOEL | 7 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Physiology (Lipid peroxidation) | LOEC | 15 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Biochemistry (Metallothionein) | LOEC | 7 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Accumulation (Residue) | LOEC | 3 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | LOEC | 10 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Mortality | LOEL | 14 | days | 0.3484 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Basommatophora | Mortality | 8 | days | 50 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Howard,T.E., H.N. Halvorson, and C.C. Walden | Toxicity of Copper Compounds to the Snail Vector Hosts of the Agent of Schistosoma Dermatitis, in Waters of Differing Hardness | Am. J. Hyg.80:33-44 | 1964 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Basommatophora | Mortality | 8 | days | 10 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Howard,T.E., H.N. Halvorson, and C.C. Walden | Toxicity of Copper Compounds to the Snail Vector Hosts of the Agent of Schistosoma Dermatitis, in Waters of Differing Hardness | Am. J. Hyg.80:33-44 | 1964 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Basommatophora | Mortality | 3 | days | 10 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Howard,T.E., H.N. Halvorson, and C.C. Walden | Toxicity of Copper Compounds to the Snail Vector Hosts of the Agent of Schistosoma Dermatitis, in Waters of Differing Hardness | Am. J. Hyg.80:33-44 | 1964 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.2332 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.2266 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.2266 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Hediste diversicolor | Accumulation (Residue) | LOEC | 7 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Mortality | 14 | days | 0.2332 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Mortality | 14 | days | 0.02092 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Mortality | 14 | days | 0.15336 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | NOEC | 14 | days | 0.2266 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | NOEC | 14 | days | 0.15336 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | NOEC | 14 | days | 0.02092 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Mortality | 15 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Hediste diversicolor | Enzyme(s) (Catalase) | LOEC | 7 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.3484 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.3484 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.3484 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.3484 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.2266 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.3484 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.2266 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Accumulation (Residue) | LOEC | 14 | days | 0.3484 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Potamopyrgus antipodarum | Mortality | LOEL | 14 | days | 0.2266 | mg/L [Labile] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pang,C., H. Selck, G.T. Banta, S.K. Misra, D. Berhanu, A. Dybowska, E. Valsami-Jones, and V.E. Forbes | Bioaccumulation, Toxicokinetics, and Effects of Copper from Sediment Spiked with Aqueous Cu, Nano-CuO, or Micro-CuO in the Deposit-Feeding Snail, Potamopyrgus antipodarum | Environ. Toxicol. Chem.32(7): 1561-1573 | 2013 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | LOEC | 1 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | LOEC | 3 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | others Morone saxatilis | Mortality | LC50 | 2 | days | 0.85 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | O'Rear,C.W.J. | The Toxicity of Zinc and Copper to Striped Bass Eggs and Fry with Methods for Providing Confidence Limits | Proc. Southeast. Assoc. Game Fish Comm.26:484-489 | 1972 | 2019/02/13 | ||||||
| 魚類 | others Morone saxatilis | Mortality | LC50 | 2 | days | 0.74 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | O'Rear,C.W.J. | The Toxicity of Zinc and Copper to Striped Bass Eggs and Fry with Methods for Providing Confidence Limits | Proc. Southeast. Assoc. Game Fish Comm.26:484-489 | 1972 | 2019/02/13 | ||||||
| 魚類 | others Morone saxatilis | Mortality | LC50 | 2 | days | 0.31 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | O'Rear,C.W.J. | The Toxicity of Zinc and Copper to Striped Bass Eggs and Fry with Methods for Providing Confidence Limits | Proc. Southeast. Assoc. Game Fish Comm.26:484-489 | 1972 | 2019/02/13 | ||||||
| 魚類 | others Morone saxatilis | Mortality | LC50 | 2 | days | 0.42 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | O'Rear,C.W.J. | The Toxicity of Zinc and Copper to Striped Bass Eggs and Fry with Methods for Providing Confidence Limits | Proc. Southeast. Assoc. Game Fish Comm.26:484-489 | 1972 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Growth (Weight gain) | LOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | LOEC | 5 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | LOEC | 3.79 | days | 500 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bacchetta,R., N. Santo, U. Fascio, E. Moschini, S. Freddi, G. Chirico, M. Camatini, and P. Mantecca | Nano-Sized CuO, TiO2 and ZnO Affect Xenopus laevis Development | Nanotoxicology6(1-4): 381-398 | 2012 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Growth (Length) | NOEC | 4 | days | 100 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nations,S., M. Wages, J.E. Canas, J. Maul, C. Theodorakis, and G.P. Cobb | Acute Effects of Fe2O3, TiO2, ZnO and CuO Nanomaterials on Xenopus laevis | Chemosphere83(8): 1053-1061 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Development (Stage) | NOEC | 4 | days | 1000 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nations,S., M. Wages, J.E. Canas, J. Maul, C. Theodorakis, and G.P. Cobb | Acute Effects of Fe2O3, TiO2, ZnO and CuO Nanomaterials on Xenopus laevis | Chemosphere83(8): 1053-1061 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | NOEC | 3.79 | days | 100 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bacchetta,R., N. Santo, U. Fascio, E. Moschini, S. Freddi, G. Chirico, M. Camatini, and P. Mantecca | Nano-Sized CuO, TiO2 and ZnO Affect Xenopus laevis Development | Nanotoxicology6(1-4): 381-398 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Growth (Length) | NOEC | 3.79 | days | 100 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bacchetta,R., N. Santo, U. Fascio, E. Moschini, S. Freddi, G. Chirico, M. Camatini, and P. Mantecca | Nano-Sized CuO, TiO2 and ZnO Affect Xenopus laevis Development | Nanotoxicology6(1-4): 381-398 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Growth (Length) | NOEC | 4 | days | 1 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nations,S., M. Wages, J.E. Canas, J. Maul, C. Theodorakis, and G.P. Cobb | Acute Effects of Fe2O3, TiO2, ZnO and CuO Nanomaterials on Xenopus laevis | Chemosphere83(8): 1053-1061 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Growth (Length) | LOEC | 3.79 | days | 100 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bacchetta,R., N. Santo, U. Fascio, E. Moschini, S. Freddi, G. Chirico, M. Camatini, and P. Mantecca | Nano-Sized CuO, TiO2 and ZnO Affect Xenopus laevis Development | Nanotoxicology6(1-4): 381-398 | 2012 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Development (Abnormal) | LOEC | 3.79 | days | 10 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bacchetta,R., N. Santo, U. Fascio, E. Moschini, S. Freddi, G. Chirico, M. Camatini, and P. Mantecca | Nano-Sized CuO, TiO2 and ZnO Affect Xenopus laevis Development | Nanotoxicology6(1-4): 381-398 | 2012 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Growth (Length) | LOEC | 4 | days | 1000 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nations,S., M. Wages, J.E. Canas, J. Maul, C. Theodorakis, and G.P. Cobb | Acute Effects of Fe2O3, TiO2, ZnO and CuO Nanomaterials on Xenopus laevis | Chemosphere83(8): 1053-1061 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Growth (Length) | LOEC | 4 | days | 10 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nations,S., M. Wages, J.E. Canas, J. Maul, C. Theodorakis, and G.P. Cobb | Acute Effects of Fe2O3, TiO2, ZnO and CuO Nanomaterials on Xenopus laevis | Chemosphere83(8): 1053-1061 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Development (Deformation) | EC50 | 4 | days | >1000 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nations,S., M. Wages, J.E. Canas, J. Maul, C. Theodorakis, and G.P. Cobb | Acute Effects of Fe2O3, TiO2, ZnO and CuO Nanomaterials on Xenopus laevis | Chemosphere83(8): 1053-1061 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Development (Deformation) | EC10 | 4 | days | 2.1 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nations,S., M. Wages, J.E. Canas, J. Maul, C. Theodorakis, and G.P. Cobb | Acute Effects of Fe2O3, TiO2, ZnO and CuO Nanomaterials on Xenopus laevis | Chemosphere83(8): 1053-1061 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Catalase) | LOEC | 14 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Glutathione peroxidase) | NOEC | 14 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Catalase) | NOEC | 21 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Accumulation (Residue) | NOEC | 7 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Carbonic anhydrase) | LOEC | 21 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Carbonic anhydrase) | LOEC | 14 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Accumulation (Residue) | LOEC | 21 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Glutathione peroxidase) | LOEC | 7 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Glutathione reductase) | LOEC | 14 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Glutathione peroxidase) | LOEC | 14 | days | 0.0143 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Catalase) | LOEC | 21 | days | 0.0143 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Glutathione reductase) | LOEC | 21 | days | 0.0396 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Accumulation (Residue) | LOEC | 3 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Accumulation (Residue) | LOEC | 7 | days | 0.0143 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Accumulation (Residue) | LOEC | 14 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena thermophila | Population (Abundance) | EC50 | 0.16 | days | 1829 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mortimer,M., K. Kasemets, and A. Kahru | Toxicity of ZnO and CuO Nanoparticles to Ciliated Protozoa Tetrahymena thermophila | Toxicology269(2/3): 182-189 | 2010 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena thermophila | Population (Abundance) | EC50 | 1 | days | 2314 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mortimer,M., K. Kasemets, and A. Kahru | Toxicity of ZnO and CuO Nanoparticles to Ciliated Protozoa Tetrahymena thermophila | Toxicology269(2/3): 182-189 | 2010 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena thermophila | Mortality | EC50 | 1 | days | 1966 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mortimer,M., K. Kasemets, and A. Kahru | Toxicity of ZnO and CuO Nanoparticles to Ciliated Protozoa Tetrahymena thermophila | Toxicology269(2/3): 182-189 | 2010 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena thermophila | Mortality | EC50 | 1 | days | 97.9 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mortimer,M., K. Kasemets, and A. Kahru | Toxicity of ZnO and CuO Nanoparticles to Ciliated Protozoa Tetrahymena thermophila | Toxicology269(2/3): 182-189 | 2010 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena thermophila | Population (Abundance) | EC50 | 0.16 | days | 129 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mortimer,M., K. Kasemets, and A. Kahru | Toxicity of ZnO and CuO Nanoparticles to Ciliated Protozoa Tetrahymena thermophila | Toxicology269(2/3): 182-189 | 2010 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena thermophila | Population (Abundance) | EC50 | 1 | days | 101 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mortimer,M., K. Kasemets, and A. Kahru | Toxicity of ZnO and CuO Nanoparticles to Ciliated Protozoa Tetrahymena thermophila | Toxicology269(2/3): 182-189 | 2010 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena thermophila | Mortality | EC50 | 0.16 | days | 127 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mortimer,M., K. Kasemets, and A. Kahru | Toxicity of ZnO and CuO Nanoparticles to Ciliated Protozoa Tetrahymena thermophila | Toxicology269(2/3): 182-189 | 2010 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena thermophila | Mortality | EC50 | 0.16 | days | 1580 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mortimer,M., K. Kasemets, and A. Kahru | Toxicity of ZnO and CuO Nanoparticles to Ciliated Protozoa Tetrahymena thermophila | Toxicology269(2/3): 182-189 | 2010 | 2019/02/13 | ||||||
| 魚類 | others Gambusia affinis | Mortality | LC50 | 4 | days | >56000 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wallen,I.E., W.C. Greer, and R. Lasater | Toxicity to Gambusia affinis of Certain Pure Chemicals in Turbid Waters | Sewage Ind. Wastes29(6): 695-711 | 1957 | 2019/02/13 | ||||||
| 魚類 | others Gambusia affinis | Mortality | LC50 | 2 | days | >56000 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wallen,I.E., W.C. Greer, and R. Lasater | Toxicity to Gambusia affinis of Certain Pure Chemicals in Turbid Waters | Sewage Ind. Wastes29(6): 695-711 | 1957 | 2019/02/13 | ||||||
| 魚類 | others Gambusia affinis | Mortality | LC50 | 1 | days | >56000 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wallen,I.E., W.C. Greer, and R. Lasater | Toxicity to Gambusia affinis of Certain Pure Chemicals in Turbid Waters | Sewage Ind. Wastes29(6): 695-711 | 1957 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Glutathione peroxidase) | LOEC | 21 | days | 0.0143 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Glutathione reductase) | NOEC | 21 | days | 0.0143 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Brachionus calyciflorus | Mortality | LC50 | 1 | days | 0.39 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 28 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Brachionus calyciflorus | Mortality | LC50 | 1 | days | 0.24 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manusadzianas,L., C. Caillet, L. Fachetti, B. Gylyte, R. Grigutyte, S. Jurkoniene, R. Karitonas, K. Sadauskas, F. Thoma | Toxicity of Copper Oxide Nanoparticle Suspensions to Aquatic Biota | Environ. Toxicol. Chem.31(1): 108-114 | 2012 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 15 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Aiptasia pallida | Enzyme(s) (Glutathione peroxidase) | NOEC | 21 | days | 0.00443 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Siddiqui,S., R.H. Goddard, and G.K. Bielmyer-Fraser | Comparative Effects of Dissolved Copper and Copper Oxide Nanoparticle Exposure to the Sea Anemone, Exaiptasia pallida | Aquat. Toxicol.160:205-213 | 2015 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 25 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 17.5 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | NOEC | 25 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | NOEC | 15 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | NOEC | 1 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | NOEC | 25 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | NOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | NOEC | 20 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | NOEC | 15 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | NOEC | 20 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Growth (Weight gain) | NOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Growth (Length) | NOEC | 30 | days | 0.0128 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 6 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 10 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 3 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 20 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | LOEC | 3 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | LOEC | 5 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 1 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | LOEC | 1 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 17.5 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation (Residue) | LOEC | 5 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 15 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 21 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 28 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 3 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 14 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 21 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 21 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 12 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 10.5 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 9 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 10.5 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 14 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 10.5 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme(s) (Cholinesterase) | NOEC | 30 | days | 0.01465 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 12 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 7 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 9 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 5 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 17.5 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 3 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 24.5 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 28 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 24.5 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth (Specific growth rate) | NOEC | 28 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 24.5 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 15 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 15 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 14 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth (Specific growth rate) | NOEC | 15 | days | 292.8 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation (Residue) | NOEC | 7 | days | 411.9 | その他others [mg/kg food, Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Physiology (Lipid peroxidation) | NOEC | 3 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Acetylcholinesterase) | NOEC | 3 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Acetylcholinesterase) | NOEC | 7 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Glutathione peroxidase) | NOEC | 3 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Biochemistry (Metallothionein) | NOEC | 3 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Superoxide dismutase (SOD) enzyme activity) | NOEC | 3 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Glutathione peroxidase) | NOEC | 3 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Physiology (Lipid peroxidation) | NOEC | 3 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Scrobicularia plana | Biochemistry (Metallothionein) | NOEC | 16 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Catalase) | NOEC | 15 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Accumulation (Residue) | NOEC | 7 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Catalase) | NOEC | 3 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Glutathione peroxidase) | LOEC | 15 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Glutathione peroxidase) | LOEC | 7 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Biochemistry (Metallothionein) | LOEC | 15 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Physiology (Lipid peroxidation) | LOEC | 15 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Superoxide dismutase (SOD) enzyme activity) | LOEC | 15 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Physiology (Lipid peroxidation) | LOEC | 7 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Superoxide dismutase (SOD) enzyme activity) | LOEC | 7 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Scrobicularia plana | Feeding behavior (Food consumption) | LOEC | 11 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Scrobicularia plana | Enzyme(s) (Catalase) | LOEC | 16 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Scrobicularia plana | Behavior (Burrowing behavior, burrowing length) | LOEC | 4 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Scrobicularia plana | Accumulation (Residue) | LOEC | 16 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Scrobicularia plana | Enzyme(s) (Glutathione S-transferase) | LOEC | 16 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Scrobicularia plana | Enzyme(s) (Superoxide dismutase (SOD) enzyme activity) | LOEC | 16 | days | 0.01 | mg/L [Dissolved] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buffet,P.E., O.F. Tankoua, J.F. Pan, D. Berhanu, C. Herrenknecht, L. Poirier, C. Amiard-Triquet, J.C. Amiard, J.B. Bera | Behavioural and Biochemical Responses of Two Marine Invertebrates Scrobicularia plana and Hediste diversicolor to Copper Oxide Nanoparticles | Chemosphere84(1): 166-174 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Superoxide dismutase (SOD) enzyme activity) | LOEC | 15 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | NOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Accumulation (Residue) | LOEC | 3 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Glutathione peroxidase) | LOEC | 15 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Physiology (Lipid peroxidation) | LOEC | 7 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Biochemistry (Metallothionein) | LOEC | 15 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Catalase) | LOEC | 15 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Biochemistry (Metallothionein) | LOEC | 3 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Superoxide dismutase (SOD) enzyme activity) | LOEC | 7 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Accumulation (Residue) | LOEC | 15 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Catalase) | LOEC | 7 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Catalase) | LOEC | 7 | days | 0.01 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., C.G. Pereira, C. Cardoso, J.P. Pinheiro, I. Cancio, and M.J. Bebianno | Accumulation and Toxicity of Copper Oxide Nanoparticles in the Digestive Gland of Mytilus galloprovincialis | Aquat. Toxicol.118/119:72-79 | 2012 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Enzyme(s) (Acetylcholinesterase) | LOEC | 15 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 6 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 12 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 18 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Anodonta anatina | Accumulation (Residue) | LOEC | 24 | days | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nugroho,A.P., and H. Frank | Uptake, Distribution, and Bioaccumulation of Copper in the Freshwater Mussel Anodonta anatina | Toxicol. Environ. Chem.93(9): 1838-1850 | 2011 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Mytilus galloprovincialis | Biochemistry (Metallothionein) | LOEC | 7 | days | 0.0048 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gomes,T., J.P. Pinheiro, I. Cancio, C.G. Pereira, C. Cardoso, and M.J. Bebianno | Effects of Copper Nanoparticles Exposure in the Mussel Mytilus galloprovincialis | Environ. Sci. Technol.45(21): 9356-9362 | 2011 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 12 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 21 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 14 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 24.5 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 24.5 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 7 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 3 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 12 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 15 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 11 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | NOEC | 15 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 6 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 9 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 28 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 11 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 21 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 28 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 24.5 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 5 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 15 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 9 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 28 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 15 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 21 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | NOEC | 28 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 17.5 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 14 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 17.5 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 14 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 17.5 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 11 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 3 | days | 292.8 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | NOEC | 7 | days | 411.9 | ppm [TOTAL] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2018/03/15 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | NOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Growth | NOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | NOEC | 15 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | NOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | NOEC | 20 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | NOEC | 25 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | NOEC | 1 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | NOEC | 15 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | NOEC | 25 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Growth | NOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | NOEC | 20 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Growth | LOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | LOEC | 3 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | LOEC | 1 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | LOEC | 1 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | LOEC | 5 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Growth | LOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | LOEC | 3 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | LOEC | 10 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | LOEC | 5 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 15 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Enzyme | LOEC | 10 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 30 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 20 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 10 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 5 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 25 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 12.8 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 3 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Accumulation | LOEC | 1 | days | 14.65 | μg/L [DISSOLVED] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2018/03/09 | ||||||
| 魚類 | Cyprinus carpio (Carp) | Behavior | 10～60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 411.9 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2016/03/25 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 7 | days | 411.9 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 3.5 | days | 411.9 | ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2016/03/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | 4 | days | 10～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2016/03/25 | ||||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | 4 | days | 10～60 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2016/03/25 | ||||||||
| 魚類 | Cyprinus carpio (Carp) | Behavior | 10～<40 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zhao,J., Z. Wang, X. Liu, X. Xie, K. Zhang, and B. Xing | Distribution of CuO Nanoparticles in Juvenile Carp (Cyprinus carpio) and Their Potential Toxicity | J. Hazard. Mater.197:304-310 | 2011 | 2016/03/25 | ||||||||||
| 魚類 | Oncorhynchus mykiss | Growth (Specific growth rate) | NOEC | 15 | days | 292.8 | μg/g | 16 ECOTOX | Kjoss,V.A., C.M. Wood, and D.G. McDonald | Effects of Different Ligands on the Bioaccumulation and Subsequent Depuration of Dietary Cu and Zn in Juvenile Rainbow Trout (Oncorhynchus mykiss) | Can. J. Fish. Aquat. Sci.63(2): 412-422 | 2006 | 2022/01/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | L(E)C50 | 2837 | その他others [μgCu/L] | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 468.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1564 | 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 | 363.6 | 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 | 422.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 2034 | 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 | 19.1 | 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 | 402.4 | 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 | 613.3 | 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 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1959 | 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 | 129 | 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 | 96.6 | 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 | 106.1 | 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 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 494.8 | 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 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 59 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 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 | 48 | hours | 13.2 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 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 | 12 ECHA Information on Registered Substances | 2 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 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 | 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 | Marr, J.C.A. et al. | Relationship between copper exposure duration, tissue copper concentration and rainbow trout growth | Aquatic Toxicol. 36, 17-30 | 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 | Seim, W.K. et al. | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously or intermittently exposure to copper | Can. J. Fish. Aquat. Sci. Vol. 41, 433-438 | 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 | 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 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1514 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 671.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1405 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 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 | 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 | Pimephales promelas | mortality | LC50 | 96 | hours | 1390 | 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 | 473 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | 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 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 96 | hours | 13 | μg/L [meas. (TWA) element] | ○ | 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 | 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 | 230 | 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 | 470 | μg/L [nominal element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Cyprinus carpio | mortality | LC50 | 96 | hours | 820 | μg/L [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 | 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 | 22 | 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 | 17.4 | 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 | 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 | 197 | 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 | 544 | 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 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 1870 | 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 | 262 | 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 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 684 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 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 | Bossuyt BTA, De Schamphelaere KAC, Janssen CR | Using the biotic ligand model for predicting the acute sensitivity of cladoceran dominated communities to copper in natural surface waters | Environmental Science and Technology 38:5030-5037 | 2021/10/25 | |||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 212.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 24 | 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 | 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 | Pimephales promelas | mortality | LC50 | 96 | hours | 180 | 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 | 48 | hours | 7.5 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >55.1 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | 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 | 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 | Waiwood, K.G. & Beamish, F.W.H. | The effect of copper, hardness and pH on the growth of rainbow trout, Salmo gairdneri | Journal of Fish Biology 13, 591-598 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 383.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 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 | 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 | NOEC | 96 | hours | 13.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | >24.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 48 | hours | 15.3 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 48 | hours | 24.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 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 | 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 | 48 | hours | 12.8 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 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 AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 148.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 48 | hours | 7.2 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 48 | hours | 10.2 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | 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 | Pimephales promelas | mortality | LC50 | 96 | hours | 390 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 360 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 410 | μg/L [meas. element] | ○ | 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 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 148.4 | 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 | |||||
| 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 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 212.1 | μg/L [meas. 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 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 11.66 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | Nimmo DWR, Johnson RW, Preul MA, Pillsbury RW, Self JR, Bergey EA | Determining site-specific toxicity of copper to daphnids and fishes in a brown-water ecosystem | Journal of Freshwater Ecology 21(3):481-491 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 48 | hours | 5.9 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 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 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 726.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 597.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 48 | hours | 21.4 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 48 | hours | 30.2 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 2021/10/25 | ||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 48 | hours | 7.8 | μg/L [meas. element] | 12 ECHA Information on Registered Substances | 1 | Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of copper exposure on whole-body sodium levels in larval fathead minnows (Pimephales promelas) | Environmental Toxicology and Chemistry 27(6):1442-1449 | 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 | Ryan AC, Van Genderen EJ, Tomasso JR, Klaine SJ | Influence of natural organic matter source on copper toxicity to larval fathead minnows (Pimephales promelas): implications for the biotic ligand model | Environmental Toxicology and Chemistry 23(6):1567-1574 | 2021/10/25 | |||||
| 魚類 | Danio rerio (previous name: Brachydanio rerio) | mortality | LC50 | 96 | hours | 11.66 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | 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 | 429 | 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 | 774.3 | 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 | LC50 | 96 | hours | 102 | μg/L [meas. 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 | |||||
| 魚類 | Pimephales promelas | mortality | LC50 | 96 | hours | 596.3 | 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 | 283.6 | 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 | 19.1 | 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) | mortality + immobility combined | LC50 | 96 | hours | 60 | 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 | 60.6 | 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) | mortality | LC50 | 96 | hours | 36.5 | 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 | 6.7 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | LC50 | 96 | hours | 8.5 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | publication | 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 | publication | 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 | publication | 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 | publication | 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 | 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 | 30.9 | 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 | 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 + immobility combined | LC50 | 96 | hours | 63 | 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 | 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 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 460 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2018/02/17 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 710 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1954 | 2018/02/17 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 770 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1954 | 2018/02/17 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 1000 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1980 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 450 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 155.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 189.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 171 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 490 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 645 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 166.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 160.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 158.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 21.5 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 151 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 12.5 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 164 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 298 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 47.4 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 81.1 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 29 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 21 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 152 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 16.5 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 297 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 35 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 28 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 4.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 12.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 42.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 311 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 62.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 193 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/09 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 150.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 148.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 758.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 513 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 197 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 5.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 18.2 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 752.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 698 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 996.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 905.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 42.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 514 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 165 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 168.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 19.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 68.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 62.5 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 243 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 860 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >200 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 44 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 15 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 96 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 85.3 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/10 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 169 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/10 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 890 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1973 | 2018/03/09 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 690 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 840 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 79.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 730 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 770 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 630 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 980 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 930 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 830 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Cyprinus carpio (Carp) | mortality | LC50 | 96 | hours | 800 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 870 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 23.2 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Cyprinus carpio (Carp) | mortality | LC50 | 96 | hours | 810 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1971 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 68 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 93 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | >89 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/12 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 81.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 78.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 77.5 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 57 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 136.5 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 21.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 20.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 17.2 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 12.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 20.5 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 663 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 71.2 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 600 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/09 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 274 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/10 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 75 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1969 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 84 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1969 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 470 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1968 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 10.5 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 9.5 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 18 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1998 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 103 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/10 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 9150 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/11 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 309 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 30 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 18 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 17 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 28 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 221 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 128 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/10 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 83.3 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/10 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 229.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/09 | ||||||
| 魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 35 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1982 | 2018/03/09 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 410 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2018/02/17 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 360 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2018/02/17 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 390 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2018/02/17 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 210 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2018/02/17 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 1100 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1975 | 2018/02/17 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 38.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/09 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 232 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 230 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/09 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 80 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1984 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 31.9 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 82.2 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 70 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 40 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 22.4 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 28.9 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 253 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 256.2 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/09 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 181 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 644.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 646.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 653.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 190.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 4300 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 650 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 127.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 182.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 405.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 176.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 175.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 143 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 137.2 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 132.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 131.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 129.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 865 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 271.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 191.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 199.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 223.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 226.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 242.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 253.5 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 262.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 521 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 496 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 200 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 283.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 289.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 289.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 292.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 370.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 4250 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 268.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 111.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 84.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 600 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 114.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | <640 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 123.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 122.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 117.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 83.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 113.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 110.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 103.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 101.5 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 99.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 97.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 96.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 94 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 190.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 126.6 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 125.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >830 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 650 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | <=560 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 760 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 125.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 580 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 122.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 680 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 210 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 690 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 190 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 920 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 940.4 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 645 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/11 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 94 | μg/L [element] | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/03/12 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 2.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2018/03/11 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 516 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/17 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 77 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 810 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 940 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1060 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >800 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 950 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 660 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 102 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 363 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/03/11 | ||||||
| 魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 149 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 970 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 92.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 75.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.8 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.5 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 58.5 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 52.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 46.3 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 44.7 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 41.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 36.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.9 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 892.1 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 953 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 112 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 960 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 4.2 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 390 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1981 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 286 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 52 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 427 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >449 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/03/11 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 430 | μg/L [element] | × | 12 ECHA Information on Registered Substances | 2 | publication | 1968 | 2018/02/17 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1000 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 465 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/11 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1400 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 830 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 920 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >810 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1090 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >610 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 640 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 780 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >800 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >780 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 490 | μg/L [dissolved] | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/17 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 25.4 | ppm | 3 USEPA Pesticide Ecotoxicity Database | J. Sylvester | 1997 | 2018/02/20 | |||||||||
| 魚類 | Cyprinodon variegatus | number hatched | NOEC | 7 | days | 109 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | 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 | 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 | 2021/10/25 | |||||||||
| 魚類 | Cyprinodon variegatus | embryo development (weight) | NOEC | 32 | days | 57.8 | μg/L [meas. (arithm. mean) dissolved] | 12 ECHA Information on Registered Substances | 1 | 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 | 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 | ||||||
| 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 | publication | 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) | dry weight | EC10 | 52 | days | 45.5 | 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) | larval fish 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) | larval fish survival | EC10 | 52 | days | 54.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | ||||||
| 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 | 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 | ||||||
| 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 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | wet weight | EC10 | 52 | days | 36 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | publication | 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 | publication | 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 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | wet biomass | EC10 | 52 | days | 28.2 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | overall survival | EC10 | 52 | days | 28.5 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | 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 | ||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | NOEC | 7 | days | 23.2 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 7 | days | 29.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | 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 | 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 | NOEC | 7 | days | 15.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC10 | 7 | days | 22 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC50 | 7 | days | 44.6 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | NOEC | 7 | days | 15.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC10 | 7 | days | 19.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC50 | 7 | days | 35.4 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC50 | 7 | days | 15.8 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | 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 | 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 | mortality | LC10 | 7 | days | 18.9 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | publication | 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 | publication | 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 | publication | 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 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 7 | days | 41 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC50 | 7 | days | 37.4 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | 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) | biomass | EC10 | 52 | days | 30 | μg/L [meas. 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 | Pimephales promelas | mortality | NOEC | 7 | days | 11.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 4 | days | 54.7 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 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) | dry biomass | EC10 | 52 | days | 38.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 7 | days | 8.7 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC10 | 7 | days | 10.1 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 7 | days | >12.8 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | NOEC | 7 | days | 8.7 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry 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) | all endpoints covered (see EC10 results) | NOEC | 52 | days | 24.5 | 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 | 8.7 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC50 | 7 | days | 24.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry biomass | EC50 | 7 | days | 12.8 | μg/L [meas. (TWA) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | 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 | mortality | LC10 | 7 | days | >11.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight and mean dry biomas | NOEC | 7 | days | 11.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC50 | 7 | days | >11.9 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 7 | days | 13.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | LC10 | 7 | days | 13.8 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | 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 | 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 | EC10 | 7 | days | 18.7 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | growth, mean dry weight | EC50 | 7 | days | 27.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | NOEC | 4 | days | 22.9 | μg/L [meas. (TWA) element (dissolved fraction)] | ○ | 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 | 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 | 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 | ||||||
| 魚類 | Pimephales promelas | 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 | ||||||||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | ||||||||||||||
| 魚類 | Pimephales promelas | mean number of eggs per female | NOEC | 187 | days | 25.5 | μg/L [meas. (arithm. mean) Total Cu] | 12 ECHA Information on Registered Substances | 2 | 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 | 47.13 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 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 | EC10 | 30 | days | 19 | μg/L [meas. 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 | 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 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | weight | EC10 | 30 | days | 10 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | mortality | EC10 | 30 | days | 19 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | biomass | EC10 | 30 | days | 15 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | 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 | 97 | days | 23 | μg/L [meas. (arithm. mean) Total 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 | NOEC | 28 | days | 61 | μg/L [meas. (arithm. mean) mean total copper] | 12 ECHA Information on Registered Substances | 2 | Besser JM, Wang N, Dwyer FJ, Mayer FL, Ingersoll CG | Assessing contaminant sensitivity of endangered and threatened aquatic species: Part II. Chronic toxicity of copper and pentachlorophenol to two endangered species and two surrogate species | Archives of Environmental Contamination and Toxicology 48:155-165 | 2021/10/25 | ||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 17 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 3 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | Fundulus heteroclitus | 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 | 47.13 | μg/L [meas. (arithm. mean) Total + Labile Cu] | 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 | ||||||
| 魚類 | Pimephales promelas | 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 | ||||||||||||
| 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 | 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 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | weight | EC10 | 30 | days | 16 | μg/L [meas. 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 | study report | 2021/10/25 | |||||||
| 魚類 | Pimephales promelas | biomass | EC10 | 30 | days | 6.9 | μg/L [meas. 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 | 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) | biomass | EC10 | 30 | days | 4.8 | 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 | EC10 | 30 | days | 3.9 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC20 | 21 | days | 36 | 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 | EC20 | 21 | days | 47 | 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) | weight | EC10 | 30 | days | 8.4 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | dry weight | EC20 | 28 | days | 43 | 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 | EC20 | 52 | days | 36 | 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 | EC20 | 21 | days | 43 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | study report | 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 | 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) | length | EC10 | 52 | days | >59 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 16.1 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | 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 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | mortality | EC10 | 30 | days | 7.6 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 3 | study report | 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 | study report | 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 | study report | 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 | 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 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | overall survival | EC10 | 52 | days | 49.3 | μg/L [meas. (arithm. mean) element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | study report | 2021/10/25 | |||||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 16 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 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 | publication | 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 | publication | 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 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 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | weight | EC10 | 30 | days | >22 | 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, wet weight | NOEC | 28 | days | 27 | μg/L [meas. 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 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 30 | days | 15 | 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, biomass | NOEC | 52 | days | 28 | μg/L [meas. element] | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 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 | Heijerick DG, Bossuyt BTA, De Schamphelaere KAC, Indeherberg M, Mingazzini M, Janssen CR | Effect of varying physicochemistry of European surface waters on the copper toxicity to the green alga Pseudokirchneriella subcapitata | Ecotoxicology, 14:661-670 | 2021/10/25 | |||||
| 魚類 | Oncorhynchus mykiss (previous name: Salmo gairdneri) | biomass | EC10 | 21 | days | 31 | 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 | EC10 | 28 | days | 34 | 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) | wet weight | EC10 | 28 | days | 13 | 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) | mortality | NOEC | 61 | days | 28 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials Materials and methods Test guideline | 1993 | 2018/02/17 | ||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 61 | days | 24 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials Materials and methods Test guideline | 1993 | 2018/03/09 | ||||
| 魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 32 | days | 4.8 | μg/L | × | 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 | 1985 | 2018/02/17 | ||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 78 | days | 16 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Seim, W.K. et al. | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously or intermittently exposure to copper | Can. J. Fish. Aquat. Sci | 1984 | 2018/02/17 | ||||
| 魚類 | Pimephales promelas (Fathead minnow) | growth rate | 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 | 1968 | 2018/03/09 | ||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 45 | days | 11.4 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | McKim J.M., J.G. Eaton and G.W. Holcombe | Metal toxicity to embryos and larvae of eight species of freshwater fish - II: copper | 0007-4861/78/0019-0608 Springer-Verlag New York Inc. | 1978 | 2018/03/09 | ||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 60 | days | 2.2 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Marr, J.C.A. et al. | Relationship between copper exposure duration, tissue copper concentration and rainbow trout growth | Aquatic Toxicol | 1996 | 2018/02/17 | ||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 96 | hours | 294 | μg/L | 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 | 2018/03/08 | ||||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 96 | hours | 18 | μg/L | 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 | 2018/03/08 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | number of eggs/spawn | NOEC | 270 | days | 66 | μg/L [dissolved] | × | 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 | 1976 | 2018/02/17 | ||||
| 魚類 | Pimephales promelas (Fathead minnow) | 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 | 1968 | 2018/03/09 | ||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 32 | days | 4.8 | μg/L | × | 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 | 1985 | 2018/02/17 | ||||
| 魚類 | Pimephales promelas (Fathead minnow) | growth rate | 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. | 1969 | 2018/02/17 | ||||
| 魚類 | Pimephales promelas (Fathead minnow) | 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. | 1969 | 2018/02/17 | ||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 61 | days | 45 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials Materials and methods Test guideline | 1993 | 2018/03/09 | ||||
| 魚類 | Pimephales promelas (Fathead minnow) | 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. | 1969 | 2018/02/17 | ||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 96 | hours | >963 | μg/L | 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 | 2018/02/17 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 45 | days | 11.4 | μg/L [dissolved] | × | 12 ECHA Information on Registered Substances | 2 | McKim J.M., J.G. Eaton and G.W. Holcombe | Metal toxicity to embryos and larvae of eight species of freshwater fish - II: copper | 0007-4861/78/0019-0608 Springer-Verlag New York Inc. | 1978 | 2018/03/09 | ||||
| 魚類 | Pimephales promelas (Fathead minnow) | 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 | 1968 | 2018/03/09 | ||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | 13 | ppm | 3 USEPA Pesticide Ecotoxicity Database | J. Sylvester | 1997 | 2018/02/28 | |||||||||
| その他 | Juga plicifera | NOEC/L(E)C10 | 6 | その他others [μg Cu/L] | 4 OECD SIDS (HPVC) | 2019/03/27 |