【注意事項】
* 生態影響に係る有害性情報更新日が2019年9月以前はRead-acrossデータに○を記載しておらず、被験物質が標記の物質ではない可能性がある。
**各情報源における信頼性評価スコアの定義は下記のとおりである。
生物種 | 学名 | 影響内容 | エンドポイント | 暴露期間(値) | 暴露期間(単位) | 毒性値 | 毒性値(単位) | 毒性値(単位)種別 | 試験中の 被験物質 濃度測定 あり:○ なし:× |
情報源 | 情報源による 信頼性評価** |
著者 | タイトル | 記載誌 | 発行年 | 情報更新日 | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
subject type | scientific name | effect | endpoint | exposure duration value |
exposure duration unit |
toxicity value | toxicity unit | toxicity unit type | Read-across* | QSAR | GLP | measurement of the test material |
original work type | original work reliability rank |
author | title | referenced journal | publication year | Information update date |
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 36.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 113 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 446 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 205 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 161 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 122 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 35 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 296 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 756 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 346 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 209 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 190 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 100 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 230 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 59 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 245 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 51 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 16.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 55 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 178 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 824 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 333 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 440 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 811 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 602 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 773 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 65.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 194 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 99 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 174 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 364 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 368 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 462 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 208 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 111 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 30 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 199 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 108 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 97.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 987 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 254 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 238 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 102 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 93 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 156 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 152 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 151 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 380 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 84 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 33.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 163 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 685 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 281 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 52.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 35 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 60 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 32 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 506 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 99 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 219 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 105 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 92 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 193 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 268 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/07 | |||||
藻類 | Scenedesmus acuminatus | Population/Population change (change in N/change in time) | EC50 EC50 | 6~8 | days | 25 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Stokes,P.M. | Multiple Metal Tolerance in Copper Tolerant Green Algae | J. Plant Nutr.3(1-4) | 1981 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 59.1 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | biomass | NOEC | 72 | hours | 35.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 188 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 162 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 173 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | biomass | NOEC | 72 | hours | 19.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 48 | hours | 178 | μg/L | × | ○ | 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. 40 | 2006 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 89.2 | μg/L | × | ○ | 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 | 2003 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 99 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 170.8 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 48 | hours | 96 | μg/L | × | ○ | 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. 40 | 2006 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 40.8 | μg/L | × | ○ | 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 | 2003 | ||||
藻類 | biomass | NOEC | 72 | hours | 65.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 108 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 85 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/03/03 | ||
藻類 | biomass | NOEC | 72 | hours | 52.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 31 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/03/03 | ||
藻類 | Skeletonema costatum | growth rate | NOEC | 72 | hours | 7.54 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 110.6 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 91.3 | μg/L | × | ○ | 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 | 2003 | ||||
藻類 | Phaeodactylum tricornutum | growth rate | NOEC | 72 | hours | 5.7 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2020/03/03 | |||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 112.8 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 283 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 97.2 | μg/L | × | ○ | 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 | 2003 | ||||
藻類 | biomass | NOEC | 72 | hours | 23.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 48 | hours | 108 | μg/L | × | ○ | 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. 40 | 2006 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 54.6 | μg/L | × | ○ | 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 | 2003 | ||||
藻類 | biomass | NOEC | 72 | hours | 49 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 510 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 53.3 | μg/L | × | ○ | 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 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 67.7 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | Phaeodactylum tricornutum | growth rate | EC10 | 72 | hours | 2.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Effect of declining toxicant concentrations on algal bioassay endpoints | Simpson, S. et al. | Environmental Toxicology and Chemistry, 22(9 | 2003 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 159 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/03/03 | ||
藻類 | biomass | NOEC | 72 | hours | 56.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 19.4 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 188 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 53.7 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 63.9 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 132 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/03/03 | ||
藻類 | biomass | NOEC | 72 | hours | 17.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 111.2 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | biomass | NOEC | 72 | hours | 61.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | biomass | NOEC | 72 | hours | 15.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 84 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/03/03 | ||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 36 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 49.4 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 56 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | biomass | NOEC | 72 | hours | 94.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 37.6 | μg/L | × | ○ | 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 | 2003 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 407 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/02/28 | ||
藻類 | biomass | NOEC | 72 | hours | 164 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2020/03/03 | ||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 404 | μg/L | meas. (arithm. mean), 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. 40 | 2006 | 2020/03/03 | ||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 60.2 | μg/L | × | ○ | 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 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 174 | μg/L | × | ○ | 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 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 57.5 | μg/L | × | ○ | 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 | 2003 | 2020/03/03 | |||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 10 | days | 304 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Tisbe battagliai | Reproduction/Reproduction, general | NOEC NOEC | 8 | days | 6 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 6 | days | 66 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 10 | days | 341 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 5 | days | 129 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | Reproduction/Reproduction, general | NOEC NOEC | 10 | days | 96 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Tisbe battagliai | Mortality/Mortality | LC50 LC50 | 96 | hours | 88 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 3 | days | 208 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
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 | 2020/03/03 | |||
甲殻類 | Daphnia magna | Mortality/Mortality | LC50 LC50 | 96 | hours | 874.4 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kim,K.T., A.J. Edgington, S.J. Klaine, J.W. Cho, and S.D. Kim | Influence of Multiwalled Carbon Nanotubes Dispersed in Natural Organic Matter on Speciation and Bioavailability of Copper | Environ. Sci. Technol.43(23) | 2009 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 4 | days | 138 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Daphnia magna | Mortality/Mortality | LC50 LC50 | 96 | hours | 338 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kim,K.T., A.J. Edgington, S.J. Klaine, J.W. Cho, and S.D. Kim | Influence of Multiwalled Carbon Nanotubes Dispersed in Natural Organic Matter on Speciation and Bioavailability of Copper | Environ. Sci. Technol.43(23) | 2009 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 6 | days | 92 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 10 | days | 305 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Tisbe battagliai | Mortality/Mortality | LC50 LC50 | 96 | hours | 64 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 6 | days | 97 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
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., 21 (4) | 2002 | 2020/03/03 | |||
甲殻類 | Tisbe battagliai | development | NOEC | 21 | days | 18 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Tisbe battagliai | reproduction | NOEC | 21 | days | 18 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Tisbe battagliai | mortality | NOEC | 21 | days | 18 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Tisbe battagliai | Mortality/Mortality | NOEC NOEC | 8 | days | 10 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
甲殻類 | Tisbe battagliai | Mortality/Mortality | NOEC NOEC | 8 | days | 18 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
甲殻類 | Tisbe battagliai | Mortality/Mortality | LOEC LOEC | 8 | days | 18 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
甲殻類 | Tisbe battagliai | Mortality/Mortality | 8 | days | 24 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | |||||||
甲殻類 | Ceriodaphnia dubia | Reproduction/Reproduction, general | NOEC NOEC | 10 | days | 160 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 6 | days | 53 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | Reproduction/Reproduction, general | NOEC NOEC | 10 | days | 96 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Tisbe battagliai | Mortality/Mortality | 8 | days | 13 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | |||||||
甲殻類 | Tisbe battagliai | Reproduction/Reproduction, general | 8 | days | 8 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | |||||||
甲殻類 | Tisbe battagliai | Reproduction/Reproduction, general | LOEC LOEC | 8 | days | 10 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
甲殻類 | Tisbe battagliai | Mortality/Mortality | LOEC LOEC | 8 | days | 32 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 6 | days | 112 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Crassostrea gigas | development | NOEC | 24 | hours | 28.19 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 72 | hours | >100~<150 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosenfeldt,R.R., F. Seitz, R. Schulz, and M. Bundschuh | Heavy Metal Uptake and Toxicity in the Presence of Titanium Dioxide Nanoparticles: A Factorial Approach Using Daphnia magna | Environ. Sci. Technol.48(12) | 2014 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 48 | hours | 9.5 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schubauer-Berigan,M.K., J.R. Dierkes, P.D. Monson, and G.T. Ankley | pH-Dependent Toxicity of Cd, Cu, Ni, Pb and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus | Environ. Toxicol. Chem.12 | 1993 | ||||||
甲殻類 | Acartia tonsa | Mortality/Mortality | LC50 LC50 | 72 | hours | 9 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sosnowski,S.L., D.J. Germond, and J.H. Gentile | The Effect of Nutrition on the Response of Field Populations of the Calanoid Copepod Acartia tonsa to Copper | Water Res.13(5) | 1979 | ||||||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 48 | hours | >50~<100 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosenfeldt,R.R., F. Seitz, R. Schulz, and M. Bundschuh | Heavy Metal Uptake and Toxicity in the Presence of Titanium Dioxide Nanoparticles: A Factorial Approach Using Daphnia magna | Environ. Sci. Technol.48(12) | 2014 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 1 | days | 444 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 48 | hours | >100~<150 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosenfeldt,R.R., F. Seitz, R. Schulz, and M. Bundschuh | Heavy Metal Uptake and Toxicity in the Presence of Titanium Dioxide Nanoparticles: A Factorial Approach Using Daphnia magna | Environ. Sci. Technol.48(12) | 2014 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 48 | hours | 28 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schubauer-Berigan,M.K., J.R. Dierkes, P.D. Monson, and G.T. Ankley | pH-Dependent Toxicity of Cd, Cu, Ni, Pb and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus | Environ. Toxicol. Chem.12 | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Survival | LC50 LC50 | 48 | hours | >1~<1.5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | The Response of the Three Brood Ceriodaphnia Test to Fifteen Formulations and Pure Compounds in Common Use | Arch. Environ. Contam. Toxicol.21(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 48 | hours | 200 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schubauer-Berigan,M.K., J.R. Dierkes, P.D. Monson, and G.T. Ankley | pH-Dependent Toxicity of Cd, Cu, Ni, Pb and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus | Environ. Toxicol. Chem.12 | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 69 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2020/02/26 | |||||
甲殻類 | Mysidopsis bigelowi | Mortality/Mortality | LC50 LC50 | 96 | hours | 141 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lussier,S.M. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | U.S.EPA, Narragansett, RI | 1985 | ||||||
甲殻類 | Crassostrea virginica | Embryo development | EC50 | 48 | hours | 22.4 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 72 | hours | >50~<100 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosenfeldt,R.R., F. Seitz, R. Schulz, and M. Bundschuh | Heavy Metal Uptake and Toxicity in the Presence of Titanium Dioxide Nanoparticles: A Factorial Approach Using Daphnia magna | Environ. Sci. Technol.48(12) | 2014 | ||||||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 48 | hours | >150~<200 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosenfeldt,R.R., F. Seitz, R. Schulz, and M. Bundschuh | Heavy Metal Uptake and Toxicity in the Presence of Titanium Dioxide Nanoparticles: A Factorial Approach Using Daphnia magna | Environ. Sci. Technol.48(12) | 2014 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 2 | days | 286 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | Comparison of the Effect of Metallic Copper and Copper Nitrate (Cu(NO3)2.3H2O) on Ceriodaphnia dubia Utilizing the Three-Brood Test | Bull. Environ. Contam. Toxicol.46(1) | 1991 | ||||||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 72 | hours | >100~<150 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosenfeldt,R.R., F. Seitz, R. Schulz, and M. Bundschuh | Heavy Metal Uptake and Toxicity in the Presence of Titanium Dioxide Nanoparticles: A Factorial Approach Using Daphnia magna | Environ. Sci. Technol.48(12) | 2014 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 244 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Strongylocentrotus purpuratus | Embryo development | EC50 | 72 | hours | 14.8 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 526 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 136 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 37.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 32 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 23 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 14~17.5 | μg/L | meas. (arithm. Mean), dissolved | × | × | 12 ECHA Information on Registered Substances | 2 | 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 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2020/02/28 | ||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 22 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Dendraster excentricus | development | EC50 | 96 | hours | 34.8 | μg/L | × | × | 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. Vol.29, No2 | 2010 | ||||
甲殻類 | Dendraster excentricus | development | EC50 | 96 | hours | 28.2 | μg/L | × | × | 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. Vol.29, No2 | 2010 | ||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 63 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Dendraster excentricus | development | EC50 | 96 | hours | 6.28 | μg/L | × | × | 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. Vol.29, No2 | 2010 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 465 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 289 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 44 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 332 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 10.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 14 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Crassostrea gigas | development | NOEC | 24 | hours | 47.13 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 27 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 31 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 295 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Dendraster excentricus | development | EC50 | 96 | hours | 14.4 | μg/L | × | × | 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. Vol.29, No2 | 2010 | ||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 56 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 42 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/07 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/07 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 35.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 292 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 9.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 40 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 36 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 257 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 157 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Dendraster excentricus | Embryo development | EC50 | 48 | hours | >75.8 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 43 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 792 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Crassostrea virginica | Embryo development | EC50 | 48 | hours | 30.7 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 399 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 388 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 380 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 84 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 51 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 106 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Crassostrea virginica | Embryo development | EC50 | 48 | hours | 11.2 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 50 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Dendraster excentricus | Embryo development | EC50 | 48 | hours | 36.4 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 117 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 686 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 119 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Strongylocentrotus purpuratus | Embryo development | EC50 | 72 | hours | 24.3 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 35 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 8.5 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 70 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 9.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/07 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 58 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 109 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 484 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 91 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 421 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Crassostrea gigas | development | NOEC | 24 | hours | 19.53 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 366 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 648 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 33 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Crassostrea gigas | development | NOEC | 24 | hours | 12.83 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Crassostrea virginica | Embryo development | EC50 | 48 | hours | 40.7 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 76 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Crassostrea gigas | development | NOEC | 24 | hours | 10.89 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Mytilus edulis | development | NOEC | 48 | hours | 6.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 152 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 10 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 52 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 529 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Crassostrea gigas | development | NOEC | 24 | hours | 10.42 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2020/03/03 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 229 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 210 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Dendraster excentricus | Embryo development | EC50 | 48 | hours | 18.9 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 93 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 33.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 34 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31.8 | μg/L | meas. (not specified), element | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2020/03/03 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 175 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 8.03~9.9 | μg/L | meas. (arithm. Mean), dissolved | × | × | 12 ECHA Information on Registered Substances | 2 | 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 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2020/02/28 | ||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Strongylocentrotus purpuratus | Embryo development | EC50 | 72 | hours | 30.2 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 90 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 92.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 60 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 25 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2020/02/26 | |||||
甲殻類 | Mytilus edulis | development | EC50 | 48 | hours | 3.52~4.66 | μg/L | meas. (arithm. Mean), dissolved | × | × | 12 ECHA Information on Registered Substances | 2 | 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 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2020/02/28 | ||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 300 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 40.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Dendraster excentricus | Embryo development | EC50 | 48 | hours | 46.2 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 66 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 1213 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 188 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 21.6~25.2 | μg/L | meas. (arithm. Mean), dissolved | × | × | 12 ECHA Information on Registered Substances | 2 | 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 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2020/02/28 | ||
甲殻類 | Strongylocentrotus purpuratus | Embryo development | EC50 | 72 | hours | 46.4 | μg/L | × | × | 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. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 798 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L | meas. (not specified), element | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2020/03/03 | ||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 281 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 826 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | ||||||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 24 | hours | 70 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bellavere,C., and J. Gorbi | A Comparative Analysis of Acute Toxicity of Chromium, Copper, and Cadmium to Daphnia magna, Biomphalaria glabrata, and Brachydanio rerio | Environ. Technol. Lett.2(3) | 1981 | ||||||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 48 | hours | >100~<150 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosenfeldt,R.R., F. Seitz, R. Schulz, and M. Bundschuh | Heavy Metal Uptake and Toxicity in the Presence of Titanium Dioxide Nanoparticles: A Factorial Approach Using Daphnia magna | Environ. Sci. Technol.48(12) | 2014 | ||||||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 72 | hours | >50~<100 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rosenfeldt,R.R., F. Seitz, R. Schulz, and M. Bundschuh | Heavy Metal Uptake and Toxicity in the Presence of Titanium Dioxide Nanoparticles: A Factorial Approach Using Daphnia magna | Environ. Sci. Technol.48(12) | 2014 | ||||||
甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 EC50 | 24 | hours | 50 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bellavere,C., and J. Gorbi | A Comparative Analysis of Acute Toxicity of Chromium, Copper, and Cadmium to Daphnia magna, Biomphalaria glabrata, and Brachydanio rerio | Environ. Technol. Lett.2(3) | 1981 | ||||||
甲殻類 | Daphnia magna | Mortality/Mortality | 24 | hours | 0.27 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tomasik,P., C.H.D. Magadza, S. Mhizha, and A. Chirume | The Metal-Metal Interactions in Biological Systems. Part III. Daphnia magna | Water Air Soil Pollut.82 | 1995 | |||||||
甲殻類 | Daphnia magna | Mortality/Mortality | 24 | hours | 0.05 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tomasik,P., C.H.D. Magadza, S. Mhizha, and A. Chirume | The Metal-Metal Interactions in Biological Systems. Part III. Daphnia magna | Water Air Soil Pollut.82 | 1995 | |||||||
甲殻類 | Mysidopsis bigelowi | Mortality/Mortality | 96 | hours | 220 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lussier,S.M. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | U.S.EPA, Narragansett, RI | 1985 | |||||||
甲殻類 | Daphnia magna | Mortality/Mortality | 24 | hours | 0.15 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tomasik,P., C.H.D. Magadza, S. Mhizha, and A. Chirume | The Metal-Metal Interactions in Biological Systems. Part III. Daphnia magna | Water Air Soil Pollut.82 | 1995 | |||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | 48 | hours | >0~<0.5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | The Response of the Three Brood Ceriodaphnia Test to Fifteen Formulations and Pure Compounds in Common Use | Arch. Environ. Contam. Toxicol.21(1) | 1991 | |||||||
甲殻類 | Mytilus edulis | Behavior/Filtration rate | EC50 EC50 | 6 | hours | 30 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Manley,A.R. | The Effects of Copper on the Behaviour, Respiration, Filtration and Ventilation Activity of Mytilus edulis | J. Mar. Biol. Assoc. U.K.63 | 1983 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 48 | hours | 66 | μg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Spehar,R.L., and J.T. Fiandt | Acute and Chronic Effects of Water Quality Criteria-Based Metal Mixtures on Three Aquatic Species | Environ. Toxicol. Chem.5(10) | 1986 | ||||||
甲殻類 | Crassostrea gigas | Development/Abnormal | EC50 EC50 | 48 | hours | 22.5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Losso,C., E. His, P.F. Ghetti, and A.V. Ghirardini | Sensitivity of Embryotoxicity Test with Mytilus galloprovincialis (LMK) Towards Some Compounds of Environmental Interest (Copper and Pesticides) | Environ. Technol.25(7) | 2004 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Survival | LC50 LC50 | 3 | Brood or litter | >0~<1 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | The Response of the Three Brood Ceriodaphnia Test to Fifteen Formulations and Pure Compounds in Common Use | Arch. Environ. Contam. Toxicol.21(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) | 1990 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | NR-ZERO | 3 | Brood or litter | >0~<0.5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | The Response of the Three Brood Ceriodaphnia Test to Fifteen Formulations and Pure Compounds in Common Use | Arch. Environ. Contam. Toxicol.21(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | Reproduction/ Progeny counts/numbers | EC50 EC50 | 3 | Brood or litter | >1~<1.5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | The Response of the Three Brood Ceriodaphnia Test to Fifteen Formulations and Pure Compounds in Common Use | Arch. Environ. Contam. Toxicol.21(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 122 | 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 | 2020/03/03 | |||
甲殻類 | Neanthes arenaceodentata | growth | NOEC | 28 | days | 13.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Effect of diet on copper toxicity to Neanthes arenaceodentata | Pesch C. E., Schauer, P.S., Balboni, M.A. | NTIS PB 87-167128. pp. 369-383. In: T.M. Poston and R. Purdy (eds.). ASTM Special Technical Publication N°921: Aquatic Toxicology and Environmental Fate, Vol. 9. A Symposium Amer. Soc. Test. Mater. Philadelphia, PA, USA, 530 p. | 1986 | 2020/03/03 | |||
甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Effects of Diet on Seven-Day Ceriodaphnia dubia Toxicity Tests | Cerda, B and Olive, J.H. | Ohio J. Sci. 93 (3) | 1993 | ||||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Winner, R.W. | Water Research 19(4) | 1985 | 2020/02/26 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Winner, R.W. | Water Research 19(4) | 1985 | 2020/02/26 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 15 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Winner, R.W. | Water Research 19(4) | 1985 | 2020/02/26 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 68.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2020/03/03 | |||||
甲殻類 | Daphnia magna | mortality | NOEC | 21 | days | 36.8 | μg/L | × | ○ | 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 | 1988 | 2020/03/03 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Winner, R.W. | Water Research 19(4) | 1985 | 2020/02/26 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Winner, R.W. | Water Research 19(4) | 1985 | 2020/02/26 | |||
甲殻類 | Neanthes arenaceodentata | growth | NOEC | 28 | days | 12.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Effect of diet on copper toxicity to Neanthes arenaceodentata | Pesch C. E., Schauer, P.S., Balboni, M.A. | NTIS PB 87-167128. pp. 369-383. In: T.M. Poston and R. Purdy (eds.). ASTM Special Technical Publication N°921: Aquatic Toxicology and Environmental Fate, Vol. 9. A Symposium Amer. Soc. Test. Mater. Philadelphia, PA, USA, 530 p. | 1986 | 2020/03/03 | |||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 6.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Effects of Diet, Water Hardness and Population Source on Acute and Chronic Copper Toxicity to Ceriodaphnia dubia | Belanger, S.E. et al. | Arch. Environ. Contam. Toxicol. 18 | 1989 | 2020/02/26 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 30 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Winner, R.W. | Water Research 19(4) | 1985 | 2020/02/26 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 181 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2020/03/03 | |||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) | 1990 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 106 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2020/03/03 | |||||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 10 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Winner, R.W. | Water Research 19(4) | 1985 | 2020/02/26 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2020/03/03 | |||||
甲殻類 | Ceriodaphnia dubia | 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. 54 | 1995 | 2020/02/26 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 71.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2020/03/03 | |||||
甲殻類 | Ceriodaphnia dubia | 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. 54 | 1995 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 10 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Effects of Diet on Seven-Day Ceriodaphnia dubia Toxicity Tests | Cerda, B and Olive, J.H. | Ohio J. Sci. 93 (3) | 1993 | ||||
甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 31.6 | 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 | 2020/03/03 | |||
甲殻類 | Ceriodaphnia dubia | 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. 54 | 1995 | 2020/02/26 | |||
甲殻類 | Daphnia magna | population growth | NOEC | 21 | days | 36.8 | μg/L | × | ○ | 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 | 1988 | 2020/03/03 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 40 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Winner, R.W. | Water Research 19(4) | 1985 | 2020/02/26 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Winner, R.W. | Water Research 19(4) | 1985 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 10 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) | 1990 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | 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. 54 | 1995 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 24.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Effects of Diet, Water Hardness and Population Source on Acute and Chronic Copper Toxicity to Ceriodaphnia dubia | Belanger, S.E. et al. | Arch. Environ. Contam. Toxicol. 18 | 1989 | 2020/02/26 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 21.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2020/03/03 | |||||
甲殻類 | Daphnia magna | other: growth | NOEC | 21 | days | 12.6 | μg/L | × | ○ | 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 | 1988 | 2020/03/03 | |||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | NR-ZERO | 3 | Brood or litter | >0~<1 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cowgill,U.M., and D.P. Milazzo | The Response of the Three Brood Ceriodaphnia Test to Fifteen Formulations and Pure Compounds in Common Use | Arch. Environ. Contam. Toxicol.21(1) | 1991 | ||||||
甲殻類 | Ceriodaphnia dubia | Reproduction/ Progeny counts/numbers | 7 | days | 45 | μg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Spehar,R.L., and J.T. Fiandt | Acute and Chronic Effects of Water Quality Criteria-Based Metal Mixtures on Three Aquatic Species | Environ. Toxicol. Chem.5(10) | 1986 | |||||||
甲殻類 | Ceriodaphnia dubia | Reproduction/ Progeny counts/numbers | EC50 EC50 | 7 | days | 56 | μg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Spehar,R.L., and J.T. Fiandt | Acute and Chronic Effects of Water Quality Criteria-Based Metal Mixtures on Three Aquatic Species | Environ. Toxicol. Chem.5(10) | 1986 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Growth/Weight | EC50 EC50 | 32 | days | 11 | μg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Spehar,R.L., and J.T. Fiandt | Acute and Chronic Effects of Water Quality Criteria-Based Metal Mixtures on Three Aquatic Species | Environ. Toxicol. Chem.5(10) | 1986 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 61 | days | 24 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | In: Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | ||||
魚類 | Carassius auratus (Goldfish) | Mortality/Mortality | 4 | days | 0.000001 | M | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Isidori,M., M. Cangiano, F.A. Palermo, and A. Parrella | E-Screen and Vitellogenin Assay for the Detection of the Estrogenic Activity of Alkylphenols and Trace Elements | Comp. Biochem. Physiol. C Toxicol. Pharmacol.152(1) | 2010 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 28 | days | 61 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Scudder, B. et al. | Effects of Copper on Development of the Fathead Minnow, Pimephales promelas | Aquatic Toxicology. 12 | 1988 | ||||
魚類 | Menidia menidia (Atlantic silverside) | Mortality/Mortality | 96 | hours | 324 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cardin,J.A. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | Memo to D.Hansen, U.S.EPA, Narragansett, RI | 1985 | |||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | 48 | hours | 37.5 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | mean number of eggs per female | NOEC | 97 | days | 23 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11 | 1977 | ||||
魚類 | Menidia menidia (Atlantic silverside) | Mortality/Mortality | 96 | hours | 324 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cardin,J.A. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | Memo to D.Hansen, U.S.EPA, Narragansett, RI | 1985 | |||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | embryo development (weight) | NOEC | 32 | days | 57.8 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | number hatched | NOEC | 7 | days | 109 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
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 | ||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 61 | days | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | In: Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | ||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 61 | days | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | In: Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | ||||
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. 2 | 1968 | ||||
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. 26 | 1969 | ||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | embryo development (length) | NOEC | 32 | days | 57.8 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 61 | days | 45 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | In: Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | ||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | mortality | NOEC | 32 | days | 109 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
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. 36 | 1996 | ||||
魚類 | Pimephales promelas (Fathead minnow) | mean number of eggs per female | NOEC | 187 | days | 25.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11 | 1977 | ||||
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. 2 | 1968 | ||||
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 | ||||
魚類 | Pimephales promelas (Fathead minnow) | number of eggs/spawn | NOEC | 270 | days | 66 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Brungs, W.A. et al. | Acute and Chronic Toxicity of Copper to the Fathead Minnow in a Surface Water of Variable Quality | Water Research. 10 | 1976 | ||||
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. 26 | 1969 | ||||
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. Vol. 41 | 1984 | ||||
魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 187 | days | 69.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11 | 1977 | ||||
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. 26 | 1969 | ||||
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. 2 | 1968 | ||||
魚類 | Pimephales promelas (Fathead minnow) | mean number of eggs per female | NOEC | 7 | days | 22.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11 | 1977 | ||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | 96 | hours | 100 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Boeck,G., A. Vlaeminck, P.H.M. Balm, R.A.C. Lock, B. De Wachter, and R. Blust | Morphological and Metabolic Changes in Common Carp, Cyprinus carpio, During Short-Term Copper Exposure: Interactions Between Cu2+ and Plasma Cortisol Elevation | Environ. Toxicol. Chem.20(2) | 2001 | |||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Survival | 10 | days | 3.5 | μM | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hashemi,S., R. Blust, and G. De Boeck | The Effect of Starving and Feeding on Copper Toxicity and Uptake in Cu Acclimated and Non-Acclimated Carp | Aquat. Toxicol.86(2) | 2008 | |||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | Mortality/Mortality | NOEC NOEC | 7 | days | 120 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | Growth/Growth, general | NOEC NOEC | 7 | days | 220 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | 48 | hours | 14.5 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | |||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Survival | 10 | days | 6 | μM | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hashemi,S., R. Blust, and G. De Boeck | The Effect of Starving and Feeding on Copper Toxicity and Uptake in Cu Acclimated and Non-Acclimated Carp | Aquat. Toxicol.86(2) | 2008 | |||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | 48 | hours | 6 | μM | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | |||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | Growth/Growth, general | 7 | days | >220 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | |||||||
魚類 | Danio rerio (Zebrafish) | Mortality/Mortality | LC50 LC50 | 8 | hours | 990 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bellavere,C., and J. Gorbi | A Comparative Analysis of Acute Toxicity of Chromium, Copper, and Cadmium to Daphnia magna, Biomphalaria glabrata, and Brachydanio rerio | Environ. Technol. Lett.2(3) | 1981 | ||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | Mortality/Mortality | 7 | days | 160 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | Multiple/Multiple effects reported as one result | 32 | days | 6.2 | μg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Spehar,R.L., and J.T. Fiandt | Acute and Chronic Effects of Water Quality Criteria-Based Metal Mixtures on Three Aquatic Species | Environ. Toxicol. Chem.5(10) | 1986 | |||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | Growth/Growth, general | LOEC LOEC | 7 | days | >220 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | Mortality/Mortality | LOEC LOEC | 7 | days | 220 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 325 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality/Mortality | LC50 LC50 | 96 | hours | 96 | μg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Spehar,R.L., and J.T. Fiandt | Acute and Chronic Effects of Water Quality Criteria-Based Metal Mixtures on Three Aquatic Species | Environ. Toxicol. Chem.5(10) | 1986 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 105 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 275 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Study of Accumulation of Copper by Carp (Cyprinus carpio L.) - Adaptation Analysis of Bioconcentration by the Gills | Environ. Technol.12 | 1991 | ||||||
魚類 | Menidia menidia (Atlantic silverside) | Mortality/Mortality | LC50 LC50 | 96 | hours | 66.6 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cardin,J.A. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | Memo to D.Hansen, U.S.EPA, Narragansett, RI | 1985 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 96 | hours | 5.01 | μM | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hashemi,S., R. Blust, and G. De Boeck | The Effect of Starving and Feeding on Copper Toxicity and Uptake in Cu Acclimated and Non-Acclimated Carp | Aquat. Toxicol.86(2) | 2008 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 120 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 470 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 280 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 750 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Study of Accumulation of Copper by Carp (Cyprinus carpio L.) - Adaptation Analysis of Bioconcentration by the Gills | Environ. Technol.12 | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 275 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 930 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Leiostomus xanthurus (Spot) | Mortality/Mortality | LC50 LC50/ | 96 | hours | 280 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,D.J. | Section on Acute Toxicity Tests to be Inserted in the April 1983 Report on Site Specific FAV's | March 21st Memo from D.J.Hansen, U.S.EPA, Gulf Breeze, FL, to W.A.Brungs, U.S.EPA, Narragansette, RI | 1983 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 105 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 77.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 2.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2020/02/26 | |||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 115 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 115 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 68 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/26 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50* | 48 | hours | 1000 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rehwoldt,R., G. Bida, and B. Nerrie | Acute Toxicity of Copper, Nickel, and Zinc Ions to Some Hudson River Fish Species | Bull. Environ. Contam. Toxicol.6(5) | 1971 | ||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | Mortality/Mortality | LC50 LC50 | 96 | hours | >220 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.H., T.D. Williams, and G.J. Eales | Toxicity of Cadmium, Hexavalent Chromium and Copper to Marine Fish Larvae (Cypinodon variegatus) and Copepods (Tisbe battagliai) | Mar. Environ. Res.38(4) | 1994 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 300 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 96 | hours | 8.46 | μM | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hashemi,S., R. Blust, and G. De Boeck | The Effect of Starving and Feeding on Copper Toxicity and Uptake in Cu Acclimated and Non-Acclimated Carp | Aquat. Toxicol.86(2) | 2008 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 20.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 96 | hours | 9.2 | μM | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hashemi,S., R. Blust, and G. De Boeck | The Effect of Starving and Feeding on Copper Toxicity and Uptake in Cu Acclimated and Non-Acclimated Carp | Aquat. Toxicol.86(2) | 2008 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 289.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Poecilia reticulata (Guppy) | Mortality/Mortality | LC50 LC50 | 96 | hours | 112 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Black,J.A. | The Effect of Certain Organic Pollutants on Copper Toxicity to Fish (Lebistes reticulatus) | Ph.D.Thesis, University of Michigan, Ann Arbor, MI | 1974 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality/Mortality | LC50 LC50 | 48 | hours | 250 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bellavere,C., and J. Gorbi | A Comparative Analysis of Acute Toxicity of Chromium, Copper, and Cadmium to Daphnia magna, Biomphalaria glabrata, and Brachydanio rerio | Environ. Technol. Lett.2(3) | 1981 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 58.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 270 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 81.1 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 242.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 210 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 168.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 31.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 19.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 1100 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1975 | 2020/03/03 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 243 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 15 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/05 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 111.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 253 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 75.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 83.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 360 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 102 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 390 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 30 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 18 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1998 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 189.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 12.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 22.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 169 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 85.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 132.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 137.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 46.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 155.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 226.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 274 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 78.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 182.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 52.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 82.2 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 9150 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 970 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 223.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 52 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 112 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 166.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 450 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1400 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >800 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 650 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 540 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 490 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 38.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 770 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 256.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 860 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 20.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 42.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 35 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1982 | 2020/03/03 | |||||
魚類 | Cyprinus carpio (Carp) | mortality | LC50 | 96 | hours | 810 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1971 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 496 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 230 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 5.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 890 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1973 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 940 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 370.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 298 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 4.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 126.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 190.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 44.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 770 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1954 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1090 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 70 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 151 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 42.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 650 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 268.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 191.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 23.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >830 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >449 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 830 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 47.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 960 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 44 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/05 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 175.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 283.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 75 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1969 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 143 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 17.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 232 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 149 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 930 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1000 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 21.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 199.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 865 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 262.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 114.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/05 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 131.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 164 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 286 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 698 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 190 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 427 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 289.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 128 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 4.2 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 79.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 35 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 309 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 1000 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1980 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 410 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 136.5 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 465 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 660 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 470 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1968 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 460 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 760 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 171 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2020/03/03 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 10.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 83.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 176.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 490 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 752.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 21.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | <=560 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 630 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 17 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 253.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 41.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 9.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 4250 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 996.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 71.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 94 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 311 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >800 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 68.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 513 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2020/03/03 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 94 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/26 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 521 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 103 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 16.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 580 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 158.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 122.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 148.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 103.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 113.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 690 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 181 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 152 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 210 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 297 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2020/03/03 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 12.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 190.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 28.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 160.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 644.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | >89 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/26 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 950 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 710 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1954 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 920 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 96 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 117.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 640 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 780 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 663 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Cyprinus carpio (Carp) | mortality | LC50 | 96 | hours | 800 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 125.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >780 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >810 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 645 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 390 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1981 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 690 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 514 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 830 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 516 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 80 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1984 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 150.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 40 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 81.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 292.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | <640 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 271.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1060 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 123.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 940.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 363 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 980 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 840 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 21 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 4300 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 600 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 405.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 99.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 97.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 430 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1968 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 84.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 127.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 197 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 758.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 101.5 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 646.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 92.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >610 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 165 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 122.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 953 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 600 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 870 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 125.7 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 129.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 28 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 36.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 892.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 905.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 730 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 18.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 93 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/26 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 77 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 12.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 84 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1969 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 193 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 18 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 29 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 62.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 57 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 653.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 62.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 229.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 680 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 920 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 96.7 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 221 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 110.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/26 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 810 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/26 | |||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 275 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality/Mortality | LC50 LC50 | 24 | hours | 570 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bellavere,C., and J. Gorbi | A Comparative Analysis of Acute Toxicity of Chromium, Copper, and Cadmium to Daphnia magna, Biomphalaria glabrata, and Brachydanio rerio | Environ. Technol. Lett.2(3) | 1981 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 115 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Study of Accumulation of Copper by Carp (Cyprinus carpio L.) - Adaptation Analysis of Bioconcentration by the Gills | Environ. Technol.12 | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 135 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 475 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 750 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 110 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality/Mortality | LC50 LC50 | 96 | hours | 44 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schubauer-Berigan,M.K., J.R. Dierkes, P.D. Monson, and G.T. Ankley | pH-Dependent Toxicity of Cd, Cu, Ni, Pb and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus | Environ. Toxicol. Chem.12 | 1993 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | Mortality/Mortality | LC50 LC50 | 96 | hours | 620 | μg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Felts,P.A., and A.G. Heath | Interactions of Temperature and Sublethal Environmental Copper Exposure on the Energy Metabolism of Bluegill, Lepomis macrochirus Rafinesque | J. Fish Biol.25(4) | 1984 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality/Mortality | LC50 LC50 | 96 | hours | 15 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schubauer-Berigan,M.K., J.R. Dierkes, P.D. Monson, and G.T. Ankley | pH-Dependent Toxicity of Cd, Cu, Ni, Pb and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus | Environ. Toxicol. Chem.12 | 1993 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality/Mortality | LC50 LC50 | 96 | hours | >200 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schubauer-Berigan,M.K., J.R. Dierkes, P.D. Monson, and G.T. Ankley | pH-Dependent Toxicity of Cd, Cu, Ni, Pb and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus | Environ. Toxicol. Chem.12 | 1993 | ||||||
魚類 | Menidia menidia (Atlantic silverside) | Mortality/Mortality | LC50 LC50 | 96 | hours | 197.6 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cardin,J.A. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | Memo to D.Hansen, U.S.EPA, Narragansett, RI | 1985 | ||||||
魚類 | Menidia peninsulae | Mortality/Mortality | LC50 LC50/ | 96 | hours | 140 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hansen,D.J. | Section on Acute Toxicity Tests to be Inserted in the April 1983 Report on Site Specific FAV's | March 21st Memo from D.J.Hansen, U.S.EPA, Gulf Breeze, FL, to W.A.Brungs, U.S.EPA, Narragansette, RI | 1983 | ||||||
魚類 | Poecilia reticulata (Guppy) | Mortality/Mortality | LC50 LC50 | 96 | hours | 138 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Black,J.A. | The Effect of Certain Organic Pollutants on Copper Toxicity to Fish (Lebistes reticulatus) | Ph.D.Thesis, University of Michigan, Ann Arbor, MI | 1974 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality/Mortality | LC50 LC50 | 72 | hours | 210 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bellavere,C., and J. Gorbi | A Comparative Analysis of Acute Toxicity of Chromium, Copper, and Cadmium to Daphnia magna, Biomphalaria glabrata, and Brachydanio rerio | Environ. Technol. Lett.2(3) | 1981 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality/Mortality | LC50 LC50 | 96 | hours | 210 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bellavere,C., and J. Gorbi | A Comparative Analysis of Acute Toxicity of Chromium, Copper, and Cadmium to Daphnia magna, Biomphalaria glabrata, and Brachydanio rerio | Environ. Technol. Lett.2(3) | 1981 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50* | 96 | hours | 810 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rehwoldt,R., G. Bida, and B. Nerrie | Acute Toxicity of Copper, Nickel, and Zinc Ions to Some Hudson River Fish Species | Bull. Environ. Contam. Toxicol.6(5) | 1971 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50* | 24 | hours | 2100 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Rehwoldt,R., G. Bida, and B. Nerrie | Acute Toxicity of Copper, Nickel, and Zinc Ions to Some Hudson River Fish Species | Bull. Environ. Contam. Toxicol.6(5) | 1971 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 315 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 835 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 765 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Menidia menidia (Atlantic silverside) | Mortality/Mortality | LC50 LC50 | 96 | hours | 101.8 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cardin,J.A. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | Memo to D.Hansen, U.S.EPA, Narragansett, RI | 1985 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 275 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 850 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Menidia menidia (Atlantic silverside) | Mortality/Mortality | LC50 LC50 | 96 | hours | 155.9 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cardin,J.A. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | Memo to D.Hansen, U.S.EPA, Narragansett, RI | 1985 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 140 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 48 | hours | 955 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Peres,I., and J.C. Pihan | Copper LC50 to Cyprinus carpio. Influence of Hardness, Seasonal Variation, Proposition of Maximum Acceptable Toxicant Concentration | Environ. Technol.12(2) | 1991 | ||||||
魚類 | Cyprinus carpio (Carp) | Mortality/Mortality | LC50 LC50 | 96 | hours | 4.34 | μM | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hashemi,S., R. Blust, and G. De Boeck | The Effect of Starving and Feeding on Copper Toxicity and Uptake in Cu Acclimated and Non-Acclimated Carp | Aquat. Toxicol.86(2) | 2008 | ||||||
魚類 | Menidia menidia (Atlantic silverside) | Mortality/Mortality | LC50 LC50 | 96 | hours | 216.5 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cardin,J.A. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | Memo to D.Hansen, U.S.EPA, Narragansett, RI | 1985 | ||||||
魚類 | Menidia menidia (Atlantic silverside) | Mortality/Mortality | LC50 LC50 | 96 | hours | 97.6 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cardin,J.A. | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | Memo to D.Hansen, U.S.EPA, Narragansett, RI | 1985 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.253 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hale,J.G. | Toxicity of Metal Mining Wastes | Bull. Environ. Contam. Toxicol.17(1) | 1977 | ||||||
growth rate | NOEC | 45 | days | 11.4 | μg/L | × | ○ | 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 | ||||||
mortality | LC50 | 7 | days | 111 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | The influence of salinity and dissolved organic carbon on the toxicity of copper to the estuarine copepod, Eurytemora affinis | Hall L.W., R.D. Anderson, B.L. Lewis, W.R. Arnold | Arch Environ Contam Toxicol 54 | 2008 | |||||||
mortality | LC50 | 7 | days | 108 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | The influence of salinity and dissolved organic carbon on the toxicity of copper to the estuarine copepod, Eurytemora affinis | Hall L.W., R.D. Anderson, B.L. Lewis, W.R. Arnold | Arch Environ Contam Toxicol 54 | 2008 | |||||||
mortality | NOEC | 45 | days | 11.4 | μg/L | × | ○ | 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 | ||||||
growth rate | NOEC | 60 | days | 71.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Horning, W.B. & Neiheisel, T.W. | Chronic Effect of Copper on the Bluntnose Minnow, Pimephales notatus | Arch. Environ. Contam. Toxicol. 8 | 1979 | ||||||
Growth | NOEC | 96 | hours | 6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Redpath, K. J. | Growth Inhibition and Recovery in Mussels (Mytilus edulis) Exposed to Low Copper Concentrations | Journal of the Marine Biological Association of the United Kingdom, 65(2) | 1985 | ||||||
mortality | LC50 | 21 | days | 104 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | The influence of salinity and dissolved organic carbon on the toxicity of copper to the estuarine copepod, Eurytemora affinis | Hall L.W., R.D. Anderson, B.L. Lewis, W.R. Arnold | Arch Environ Contam Toxicol 54 | 2008 | |||||||
mortality | LC50 | 7 | days | 76.2 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | The influence of salinity and dissolved organic carbon on the toxicity of copper to the estuarine copepod, Eurytemora affinis | Hall L.W., R.D. Anderson, B.L. Lewis, W.R. Arnold | Arch Environ Contam Toxicol 54 | 2008 | |||||||
mortality | LC50 | 21 | days | 71 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | The influence of salinity and dissolved organic carbon on the toxicity of copper to the estuarine copepod, Eurytemora affinis | Hall L.W., R.D. Anderson, B.L. Lewis, W.R. Arnold | Arch Environ Contam Toxicol 54 | 2008 | |||||||
mortality | LC50 | 35 | days | 166 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | The influence of salinity and dissolved organic carbon on the toxicity of copper to the estuarine copepod, Eurytemora affinis | Hall L.W., R.D. Anderson, B.L. Lewis, W.R. Arnold | Arch Environ Contam Toxicol 54 | 2008 | |||||||
mortality | LC50 | 21 | days | 67.6 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | The influence of salinity and dissolved organic carbon on the toxicity of copper to the estuarine copepod, Eurytemora affinis | Hall L.W., R.D. Anderson, B.L. Lewis, W.R. Arnold | Arch Environ Contam Toxicol 54 | 2008 | |||||||
mortality | LC50 | 2 | days | 58.1 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | The influence of salinity and dissolved organic carbon on the toxicity of copper to the estuarine copepod, Eurytemora affinis | Hall L.W., R.D. Anderson, B.L. Lewis, W.R. Arnold | Arch Environ Contam Toxicol 54 | 2008 | |||||||
growth rate | NOEC | 30 | days | 44.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Horning, W.B. & Neiheisel, T.W. | Chronic Effect of Copper on the Bluntnose Minnow, Pimephales notatus | Arch. Environ. Contam. Toxicol. 8 | 1979 |