【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 | Population (Abundance) | EC50 | 4 | days | 0.23 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Population (Abundance) | EC50 | 4 | days | 0.06 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology (Photosynthesis) | EC50 | 0.02 | days | 0.09 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology (Photosynthesis) | EC50 | 4 | days | 1.6 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology (Photosynthesis) | EC50 | 0.02 | days | >4.5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Population (Abundance) | EC50 | 4 | days | 0.03 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology (Photosynthesis) | EC50 | 0.02 | days | 1.9 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2019/02/13 | |||||
藻類 | others Laminaria digitata | Biochemistry (Fluorescence) | NOEC | 5 | days | 0.02 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anacleto,P., F.H.M. Van Den Heuvel, C. Oliveira, R.R. Rasmussen, J.O. Fernandes, J.J. Sloth, V. Barbosa, R.N. Alves, A. | Exploration of the Phycoremediation Potential of Laminaria digitata Towards Diflubenzuron, Lindane, Copper and Cadmium in a Multitrophic Pilot-Scale Experiment | Food Chem. Toxicol.104:95-108 | 2017 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology (Photosynthesis) | EC50 | 4 | days | 1.3 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Population (Population growth rate) | IC10 | 4 | days | 0.009 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2019/02/13 | |||||
藻類 | others Laminaria digitata | Biochemistry (Fluorescence) | NOEC | 5 | days | 0.02 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anacleto,P., F.H.M. Van Den Heuvel, C. Oliveira, R.R. Rasmussen, J.O. Fernandes, J.J. Sloth, V. Barbosa, R.N. Alves, A. | Exploration of the Phycoremediation Potential of Laminaria digitata Towards Diflubenzuron, Lindane, Copper and Cadmium in a Multitrophic Pilot-Scale Experiment | Food Chem. Toxicol.104:95-108 | 2017 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Population (Population growth rate) | IC50 | 4 | days | 0.71 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2019/02/13 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | IC10 | 4 | days | 9 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology | EC50 | 0.58 | hours | 1900 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 4 | days | 710 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology | EC50 | 4 | days | 1600 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 230 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 60 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 30 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology | EC50 | 0.5 | hours | >4500 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology | EC50 | 0.5 | hours | 90 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | Physiology | EC50 | 4 | days | 1300 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2016/03/25 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 100 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 440 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 105 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 281 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 230 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 824 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 152 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 35 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 102 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 35 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 55 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 122 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 84 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 346 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 200 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 368 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 108 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 380 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 51 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 987 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 99 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 32 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 52.7 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 190 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 194 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 60 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 161 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 268 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 811 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 219 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 685 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 462 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 174 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 156 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 111 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 16.5 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 99 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 199 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 151 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 30 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 773 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Raphidocelis subcapitata | Population/Abundance | EC50 | 4 | days | 30 | μg/L | × | 16 ECOTOX | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2022/01/25 | |||||
藻類 | Raphidocelis subcapitata | Population/Population growth rate | IC50 | 96 | hours | 0.71 | mg/L | × | 16 ECOTOX | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2022/01/25 | |||||
藻類 | Raphidocelis subcapitata | Population/Abundance | EC50 | 4 | days | 230 | μg/L | × | 16 ECOTOX | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2022/01/25 | |||||
藻類 | Raphidocelis subcapitata | Population/Abundance | EC50 | 4 | days | 60 | μg/L | × | 16 ECOTOX | Versteeg,D.J. | Comparison of Short- and Long-Term Toxicity Test Results for the Green Alga, Selenastrum capricornutum | ASTM Spec. Tech. Publ.:40-48 | 1990 | 2022/01/25 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 205 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 756 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 446 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 59 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 245 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 97.4 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 296 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 193 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 92 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 333 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 364 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 506 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 254 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 208 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 93 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 163 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 602 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 36.9 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 238 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 209 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 65.4 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 33.9 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 113 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 178 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2018/02/17 | |||||
藻類 | Phaeodactylum tricornutum | NOECs/EC10 | 4 | μg/L | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
藻類 | Chlorella vulgaris | NOEC/L(E)C10 | 137 | μg Cu/L | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
藻類 | Chlorella vulgaris | NOEC(s) / EC10 | 137 | μgCu/L | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 173 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 132 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 84 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 53.7 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 99 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 94.7 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 52.9 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 174 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 60.2 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 37.6 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 36 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 91.3 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 164 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 53.3 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 15.7 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 19.3 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Phaeodactylum tricornutum | growth rate | NOEC | 72 | hours | 5.7 | μg/L | dissolved | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/02/17 | |||||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 23.1 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 112.8 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 49.4 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 97.2 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 89.2 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Skeletonema costatum | growth rate | NOEC | 72 | hours | 7.54 | μg/L | dissolved | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 19.4 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 49 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 407 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 63.9 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 108 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 85 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 56 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 283 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 35.4 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Phaeodactylum tricornutum | growth rate | EC10 | 72 | hours | 2.9 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Simpson, S. et al. | Effect of declining toxicant concentrations on algal bioassay endpoints | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 162 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Raphidocelis subcapitata | Population/Population growth rate | IC10 | 96 | hours | 0.009 | mg/L | × | 16 ECOTOX | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2022/01/25 | |||||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 65.5 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 54.6 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 110.6 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 188 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 40.8 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 61.8 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 57.5 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 17.9 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 510 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 59.1 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Selenastrum capricornutum | biomass | NOEC | 72 | hours | 56.4 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/17 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 170.8 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 111.2 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 67.7 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry | 2003 | 2018/02/17 | |||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 31 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 404 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 159 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 188 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. | 2006 | 2018/02/17 | ||||
甲殻類 | others Americamysis bahia | Mortality | NOEL | 4 | days | 0.0301 | mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2019/02/13 | ||||||
甲殻類 | others Americamysis bahia | Mortality | LC50 | 4 | days | 0.0697 | mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2019/02/13 | ||||||
甲殻類 | Daphnia magna | Mortality | LC50 | 3 | days | 0.0128 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2019/02/13 | |||||
甲殻類 | others Balanus improvisus | Mortality | LC50 | 0.5 | days | 0.7 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Koryakova,M.D., and O.M. Korn | Using Barnacle Larvae for Evaluation of the Toxicity of Antifouling Paint Compounds | Russ. J. Mar. Biol.19(3): 212-216 | 1993 | 2019/02/13 | |||||
甲殻類 | others Balanus improvisus | Mortality | LC50 | 3 | days | 0.14 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Koryakova,M.D., and O.M. Korn | Using Barnacle Larvae for Evaluation of the Toxicity of Antifouling Paint Compounds | Russ. J. Mar. Biol.19(3): 212-216 | 1993 | 2019/02/13 | |||||
甲殻類 | others Balanus improvisus | Mortality | LC50 | 1 | days | 0.5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Koryakova,M.D., and O.M. Korn | Using Barnacle Larvae for Evaluation of the Toxicity of Antifouling Paint Compounds | Russ. J. Mar. Biol.19(3): 212-216 | 1993 | 2019/02/13 | |||||
甲殻類 | others Balanus improvisus | Mortality | LC50 | 2 | days | 0.35 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Koryakova,M.D., and O.M. Korn | Using Barnacle Larvae for Evaluation of the Toxicity of Antifouling Paint Compounds | Russ. J. Mar. Biol.19(3): 212-216 | 1993 | 2019/02/13 | |||||
甲殻類 | others Balanus improvisus | Mortality | LC50 | 4 | days | 0.02 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Koryakova,M.D., and O.M. Korn | Using Barnacle Larvae for Evaluation of the Toxicity of Antifouling Paint Compounds | Russ. J. Mar. Biol.19(3): 212-216 | 1993 | 2019/02/13 | |||||
甲殻類 | Daphnia magna | Mortality | LC50 | 3 | days | 0.0504 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2019/02/13 | |||||
甲殻類 | others Daphnia similis | Mortality | EC50 | 2 | days | 0.042 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2019/02/13 | |||||
甲殻類 | others Daphnia similis | Mortality | EC10 | 2 | days | 0.012 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2019/02/13 | |||||
甲殻類 | Daphnia magna | Mortality/Mortality | LC50 | 3 | days | 50.4 | μg/L | × | 16 ECOTOX | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2022/01/25 | |||||
甲殻類 | Daphnia magna | Mortality/Mortality | LC50 | 3 | days | 12.8 | μg/L | × | 16 ECOTOX | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2022/01/25 | |||||
甲殻類 | Daphnia magna | Accumulation | 3 | days | 6.4~95.8 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2016/03/25 | ||||||||
甲殻類 | Daphnia magna | Biochemical | 3 | days | 6.4~95.8 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2016/03/25 | ||||||||
甲殻類 | Daphnia magna | Mortality | LC50 | 3 | days | 50.4 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2016/03/25 | |||||
甲殻類 | Daphnia magna | Biochemical | 3 | days | 7.4~111.5 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2016/03/25 | ||||||||
甲殻類 | Daphnia magna | Accumulation | 3 | days | 7.4~111.5 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2016/03/25 | ||||||||
甲殻類 | Daphnia magna | Mortality | LC50 | 3 | days | 12.8 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fan,W., Z. Shi, X. Yang, M. Cui, X. Wang, D. Zhang, H. Liu, and L. Guo | Bioaccumulation and Biomarker Responses of Cubic and Octahedral Cu2O Micro/Nanocrystals in Daphnia magna | Water Res.46(18): 5981-5988 | 2012 | 2016/03/25 | |||||
甲殻類 | Ceriodaphnia dubia | L(E)C50 | 34 | μgCu/L | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
甲殻類 | Mysidopsis bahia | LC50 | 96 | hours | 12 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
甲殻類 | Mysidopsis bahia | LC50 | 96 | hours | 8 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S. Hopkins | 1981 | 2018/02/20 | |||||||||
甲殻類 | Mysidopsis bahia | LC50 | 96 | hours | 69.7 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Rexrode/Montague | 1992 | 2018/02/20 | |||||||||
甲殻類 | Daphnia magna | immobilization | 48 | hours | 26 | μg/L | 10 EHC (Environmental Health Criteria) | Lewis MA | Effect of loading density on the acute toxicities of surfactants, copper, and phenol to Daphnia magna Straus. | Arch Environ Contam Toxicol | 1983 | 2018/12/13 | |||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 200 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 244 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 25 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 34 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 33 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 51 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 1213 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 66 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2018/02/15 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 295 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 40.9 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 210 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 300 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 281 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 257 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 35 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 792 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 9.8 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 388 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 465 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 798 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 58 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 529 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 37.9 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 229 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 484 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 60 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 22 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 23 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 399 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 188 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 91 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 136 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 826 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 27 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 200 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/15 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 32 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 33.8 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/15 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 50 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 93 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 35.2 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 332 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 31 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia similis | Mortality/Mortality | EC50 | 48 | hours | 0.042 | mg/L | × | 16 ECOTOX | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2022/01/25 | |||||
甲殻類 | Daphnia similis | Mortality/Mortality | EC10 | 48 | hours | 0.012 | mg/L | × | 16 ECOTOX | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2022/01/25 | |||||
甲殻類 | Americamysis bahia | Mortality/Mortality | LC50 | 96 | hours | 69.7 | ppb | 16 ECOTOX | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2022/01/25 | ||||||
甲殻類 | Americamysis bahia | Mortality/Mortality | NOEL | 96 | hours | 30.1 | ppb | 16 ECOTOX | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2022/01/25 | ||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 130 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S. Hopkins | 1981 | 2018/02/20 | |||||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 58 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 119 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 686 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 109 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 44 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 106 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 380 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 42 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 69 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2018/02/15 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 56 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 648 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 10 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/15 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 43 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 292 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 40 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/15 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 92.6 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2018/02/15 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 117 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L | element, measured average | × | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 157 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31.8 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2018/02/16 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 9.5 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/15 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2018/02/15 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 52 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 70 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/15 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 63 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 152 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 421 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 14 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 36 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 175 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 7 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/15 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 90 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | 2018/02/15 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 10.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/15 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/15 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 76 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology | 1990 | 2018/02/16 | ||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 8.5 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/15 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 84 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 366 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2018/02/15 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/15 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/15 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/15 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 20 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 26 | μg/L | 10 EHC (Environmental Health Criteria) | Lewis MA | Effect of loading density on the acute toxicities of surfactants, copper, and phenol to Daphnia magna Straus. | Arch Environ Contam Toxicol, | 1983 | 2018/03/17 | |||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 526 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 289 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2018/02/16 | ||||||
甲殻類 | others Penaeus monodon | NOECs/EC10 | 145 | μg/L | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
甲殻類 | others Ceriodaphnia dubia and Oncorhynchus mykiss | NOEC(s) / EC10 | 12 | μgCu/L | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
甲殻類 | Mysidopsis bahia | NOEL | 96 | hours | 6 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
甲殻類 | Daphnia magna | growth | NOEC | 21 | days | 12.6 | μg/L | dissolved | 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. | 1988 | 2018/02/16 | ||||
甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 3.52~4.66 | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | A comparison of the copper sensitivity of two economically important saltwater mussel species and a review of previously reported copper toxicity data for mussels: important implications for determining future ambient copper saltwater criteria for the USA | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2018/02/16 | |||||
甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 31.6 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. | 1985 | 2018/02/16 | ||||
甲殻類 | Mercenaria mercenaria | development | NOEC | 288 | hours | 7 | μg/L | 12 ECHA Information on Registered Substances | 2 | LaBreche, T.M.C. et al. | Copper Toxicity to Larval Mercenaria mercenaria (hard clam) | Environ Toxicol Chem. | 2002 | 2018/02/16 | |||||
甲殻類 | Tisbe battagliai | mortality | NOEC | 21 | hours | 18 | μg/L | dissolved | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/02/16 | |||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 6.3 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. et al. | Effects of Diet, Water Hardness and Population Source on Acute and Chronic Copper Toxicity to Ceriodaphnia dubia | Arch. Environ. Contam. Toxicol. | 1989 | 2018/02/16 | ||||
甲殻類 | Tisbe battagliai | reproduction | NOEC | 21 | hours | 18 | μg/L | dissolved | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/02/16 | |||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 24.1 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. et al. | Effects of Diet, Water Hardness and Population Source on Acute and Chronic Copper Toxicity to Ceriodaphnia dubia | Arch. Environ. Contam. Toxicol. | 1989 | 2018/02/16 | ||||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 10.42 | μg/L | Total + Labile Cu | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/02/16 | |||||
甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 30 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research | 1985 | 2018/02/16 | ||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 10 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. | 1990 | 2018/02/16 | ||||
甲殻類 | Dendraster excentricus | embryo development | EC50 | 48 | hours | 46.2 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 19.53 | μg/L | Total + Labile Cu | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 21.5 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/16 | |||||||
甲殻類 | Mytilus edulis | Growth | NOEC | 10 | days | 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 | 1985 | 2018/02/16 | ||||
甲殻類 | Strongylocentrotus purpuratus | embryo development | EC50 | 72 | hours | 14.8 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 40 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research | 1985 | 2018/02/16 | ||||
甲殻類 | Strongylocentrotus purpuratus | embryo development | EC50 | 72 | hours | 24.3 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 47.13 | μg/L | Total + Labile Cu | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/02/16 | |||||
甲殻類 | Dendraster excentricus | embryo development | EC50 | 48 | hours | >75.8 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 28.19 | μg/L | Total + Labile Cu | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/02/16 | |||||
甲殻類 | Dendraster excentricus | embryo development | EC50 | 48 | hours | 18.9 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 122 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. | 1985 | 2018/02/16 | ||||
甲殻類 | Crassostrea virginica | embryo development | EC50 | 48 | hours | 30.7 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Daphnia magna | mortality | NOEC | 21 | days | 36.8 | μg/L | dissolved | 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. | 1988 | 2018/02/16 | ||||
甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research | 1985 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 68.8 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/16 | |||||||
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 | Bioindicators and Environmental Management. Eds Jeffrey, D.W. & Madden. Academic Press | 1991 | 2018/02/16 | |||||
甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 15 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research | 1985 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 71.4 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/16 | |||||||
甲殻類 | Strongylocentrotus purpuratus | embryo development | EC50 | 72 | hours | 46.4 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Crassostrea virginica | embryo development | EC50 | 48 | hours | 22.4 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Dendraster excentricus | embryo development | EC50 | 48 | hours | 36.4 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research | 1985 | 2018/02/16 | ||||
甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 14~17.5 | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | A comparison of the copper sensitivity of two economically important saltwater mussel species and a review of previously reported copper toxicity data for mussels: important implications for determining future ambient copper saltwater criteria for the USA | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2018/02/16 | |||||
甲殻類 | Tisbe battagliai | development | NOEC | 21 | hours | 18 | μg/L | dissolved | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/02/16 | |||||
甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 8.03~9.9 | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | A comparison of the copper sensitivity of two economically important saltwater mussel species and a review of previously reported copper toxicity data for mussels: important implications for determining future ambient copper saltwater criteria for the USA | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2018/02/16 | |||||
甲殻類 | Mytilus edulis | larval development | EC50 | 48 | hours | 21.6~25.2 | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray, J. S. Cotsifas, D. S. Smith, S. Le Page and K.M. Gruenthal | A comparison of the copper sensitivity of two economically important saltwater mussel species and a review of previously reported copper toxicity data for mussels: important implications for determining future ambient copper saltwater criteria for the USA | published online in Wiley InterScience (www.interscience.wiley.com) | 2008 | 2018/02/16 | |||||
甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 4 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research | 1985 | 2018/02/16 | ||||
甲殻類 | Strongylocentrotus purpuratus | embryo development | EC50 | 72 | hours | 30.2 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 12.83 | μg/L | Total + Labile Cu | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/02/16 | |||||
甲殻類 | Crassostrea virginica | embryo development | EC50 | 48 | hours | 40.7 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 10 | μg/L | 12 ECHA Information on Registered Substances | 2 | Cerda, B and Olive, J.H. | Effects of Diet on Seven-Day Ceriodaphnia dubia Toxicity Tests | Ohio J. Sci. | 1993 | 2018/02/16 | |||||
甲殻類 | Neanthes arenaceodentata | growth | NOEC | 28 | days | 13.5 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Pesch C. E., Schauer, P.S., Balboni, M.A. | Effect of diet on copper toxicity to Neanthes arenaceodentata | T.M. Poston and R. Purdy (eds.). ASTM Special Technical Publication N°921: Aquatic Toxicology and Environmental Fate, Vol. 9. A Symposium Amer. Soc. Test. Mater. Philadelphia, PA, USA, 530 p. | 1986 | 2018/02/16 | ||||
甲殻類 | Ceriodaphnia dubia | mortality | NOEC | 7 | days | 20 | μg/L | 12 ECHA Information on Registered Substances | 2 | Cerda, B and Olive, J.H. | Effects of Diet on Seven-Day Ceriodaphnia dubia Toxicity Tests | Ohio J. Sci. | 1993 | 2018/02/16 | |||||
甲殻類 | Crassostrea virginica | embryo development | EC50 | 48 | hours | 11.2 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. | 2010 | 2018/02/18 | ||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 20 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. | 1990 | 2018/02/16 | ||||
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. | 1995 | 2018/02/16 | |||||
甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research | 1985 | 2018/02/16 | ||||
甲殻類 | Mytilus edulis | Embryo development | NOEC | 48 | hours | 6.2 | μg/L | Total dissolved + labile Cu | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/02/16 | |||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 20 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 10 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research | 1985 | 2018/02/16 | ||||
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. | 1995 | 2018/02/16 | |||||
甲殻類 | Neanthes arenaceodentata | growth | NOEC | 28 | days | 12.1 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Pesch C. E., Schauer, P.S., Balboni, M.A. | Effect of diet on copper toxicity to Neanthes arenaceodentata | T.M. Poston and R. Purdy (eds.). ASTM Special Technical Publication N°921: Aquatic Toxicology and Environmental Fate, Vol. 9. A Symposium Amer. Soc. Test. Mater. Philadelphia, PA, USA, 530 p. | 1986 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | population growth | NOEC | 21 | days | 36.8 | μg/L | dissolved | 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. | 1988 | 2018/02/16 | ||||
甲殻類 | Daphnia sp. Daphnia pulex | mortality | NOEC | 42 | days | 5 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research | 1985 | 2018/02/16 | ||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 20 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. | 1990 | 2018/02/16 | ||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 28 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/16 | |||||||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 10.89 | μg/L | Total + Labile Cu | × | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | 2018/02/16 | |||||
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. | 1995 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 181 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/16 | |||||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 106 | μg/L | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | 2018/02/16 | |||||||
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. | 1995 | 2018/02/16 | |||||
甲殻類 | Daphnia magna | NOEL | 48 | hours | 59 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S. Hopkins | 1981 | 2018/02/20 | |||||||||
甲殻類 | Daphnia magna | NOEL | 48 | hours | 30 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
甲殻類 | Mysidopsis bahia | NOEL | 96 | hours | 3 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S. Hopkins | 1981 | 2018/02/20 | |||||||||
甲殻類 | Mysidopsis bahia | NOEL | 96 | hours | 30.1 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Rexrode/Montague | 1992 | 2018/02/20 | |||||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | Mortality | LC50 | 4 | days | >0.173 | mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2019/02/13 | ||||||
魚類 | others Melanogrammus aeglefinus | Mortality | LT50 | 0.18 | days | 1.8 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Burridge,L.E., and V. Zitko | Lethality of Copper Sulfate and Copper-Treated Nets to Juvenile Haddock, Melanogrammus aeglefinus L. | Bull. Environ. Contam. Toxicol.69(3): 378-383 | 2002 | 2019/02/13 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 4 | days | 0.075 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2019/02/13 | |||||
魚類 | others Dicentrarchus labrax | Enzyme(s) (Acetylcholinesterase) | NOEC | 6 | days | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cotou,E., M. Henry, G. Rigos, and M. Alexis | Cellular Responses of the Farmed Sea Bass Dicentrarchus labrax to Copper Oxide Antifoulants | In: Proceedings of the 9th Hellenic Symposium on Oceanography and Fisheries, Patra, Greece2:1295-1302 | 2009 | 2019/02/13 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC10 | 4 | days | 0.031 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2019/02/13 | |||||
魚類 | others Melanogrammus aeglefinus | Mortality | LT50 | 0.23 | days | 1.8 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Burridge,L.E., and V. Zitko | Lethality of Copper Sulfate and Copper-Treated Nets to Juvenile Haddock, Melanogrammus aeglefinus L. | Bull. Environ. Contam. Toxicol.69(3): 378-383 | 2002 | 2019/02/13 | |||||
魚類 | Poecilia reticulata (Guppy) Biomphalaria glabrata | Mortality | LC10 | 2 | days | 0.035 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2019/02/13 | |||||
魚類 | others Dicentrarchus labrax | Immunological (Respiratory Burst activity) | NOEC | 6 | days | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cotou,E., M. Henry, G. Rigos, and M. Alexis | Cellular Responses of the Farmed Sea Bass Dicentrarchus labrax to Copper Oxide Antifoulants | In: Proceedings of the 9th Hellenic Symposium on Oceanography and Fisheries, Patra, Greece2:1295-1302 | 2009 | 2019/02/13 | ||||||
魚類 | others Dicentrarchus labrax | Biochemistry (Thiobarbituric acid reactive substances) | NOEC | 6 | days | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cotou,E., M. Henry, G. Rigos, and M. Alexis | Cellular Responses of the Farmed Sea Bass Dicentrarchus labrax to Copper Oxide Antifoulants | In: Proceedings of the 9th Hellenic Symposium on Oceanography and Fisheries, Patra, Greece2:1295-1302 | 2009 | 2019/02/13 | ||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | Mortality | NOEL | 4 | days | 0.173 | mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2019/02/13 | ||||||
魚類 | Poecilia reticulata (Guppy) Biomphalaria glabrata | Mortality | LC50 | 2 | days | 0.179 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2019/02/13 | |||||
魚類 | others Dicentrarchus labrax | Enzyme(s) (Glutathione S-transferase) | NOEC | 6 | days | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cotou,E., M. Henry, G. Rigos, and M. Alexis | Cellular Responses of the Farmed Sea Bass Dicentrarchus labrax to Copper Oxide Antifoulants | In: Proceedings of the 9th Hellenic Symposium on Oceanography and Fisheries, Patra, Greece2:1295-1302 | 2009 | 2019/02/13 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC10 | 4 | days | 31 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2016/03/25 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 4 | days | 75 | μg/L | TOTAL | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2016/03/25 | |||||
魚類 | Lepomis macrochirus (Bluegill) | L(E)C50 | 2837 | μgCu/L | 4 OECD SIDS (HPVC) | 2019/03/27 | |||||||||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 18 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1998 | 2018/02/16 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 516 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 46.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 182.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Cyprinus carpio (Carp) | mortality | LC50 | 96 | hours | 800 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | 2018/02/16 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 93 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 176.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 390 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1981 | 2018/03/12 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 181 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 126.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 810 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/12 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1060 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | >89 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/16 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 82.2 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 4.2 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2018/03/12 | |||||
魚類 | Danio rerio | Mortality/Mortality | LC50 | 96 | hours | 0.075 | mg/L | × | 16 ECOTOX | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2022/01/25 | |||||
魚類 | Cyprinodon variegatus | Mortality/Mortality | LC50 | 96 | hours | 173 | ppb | 16 ECOTOX | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2022/01/25 | ||||||
魚類 | Cyprinodon variegatus | Mortality/Mortality | NOEL | 96 | hours | 173 | ppb | 16 ECOTOX | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2022/01/25 | ||||||
魚類 | Danio rerio | Mortality/Mortality | LC10 | 96 | hours | 0.031 | mg/L | × | 16 ECOTOX | De Oliveira-Filho,E.C., R.M. Lopes, and F.J.R. Paumgartten | Comparative Study on the Susceptibility of Freshwater Species to Copper-Based Pesticides | Chemosphere56(4): 369-374 | 2004 | 2022/01/25 | |||||
魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 290 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | LC50 | 96 | hours | 312 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S. Hopkins | 1981 | 2018/02/20 | |||||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | LC50 | 96 | hours | 160 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 106 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | LC50 | 96 | hours | >173 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | 1992 | 2018/02/20 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 36.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 164 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2018/02/16 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 710 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1954 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 242.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 41.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >449 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/02/16 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 4250 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 191.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Cyprinus carpio (Carp) | mortality | LC50 | 96 | hours | 810 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1971 | 2018/02/16 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 770 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1954 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 430 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1968 | 2018/02/16 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 309 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 19.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 4.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 640 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 125.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 17 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 940.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 44.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 28 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 21 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 221 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 189.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 680 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 151 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 758.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 112 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 653.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 646.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 253.5 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 21.5 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 663 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 23.2 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 171 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 600 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 35 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 698 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 470 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1968 | 2018/02/16 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 210 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 283.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 271.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 953 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 892.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 905.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 193 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 229.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 17.2 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 274 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 128 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 600 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 970 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >800 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 780 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 42.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 630 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 175.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 58.5 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.5 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 390 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 830 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 102 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 256.2 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 81.1 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 10.5 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 752.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 127.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 190 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 230 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 1000 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1980 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 960 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 465 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >830 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 980 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 996.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 292.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 370.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 223.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 132.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 131.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 830 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 30 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 149 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 940 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 152 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 12.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 650 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 243 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 514 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1090 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 490 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >780 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 125.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 52.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 650 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | <=560 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 20.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 85.3 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 169 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 21.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/12 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 660 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/12 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 298 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 12.5 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 289.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 96 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 15 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 44 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >810 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 16.5 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 68 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 950 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 311 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 405.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 18 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >800 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 94 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/16 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 2.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 62.5 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 521 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 68.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 122.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 28 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >610 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 52 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 427 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 644.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1400 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 268.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 29 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | <640 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 5.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 920 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 150.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 62.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 143 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 168.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 18.2 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 31.9 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 690 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 200 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 496 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 148.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 690 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 103 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 83.3 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 760 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 580 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 42.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 1100 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1975 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 38.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 190.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 210 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 286 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 460 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2018/03/12 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 129.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 9.5 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 297 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2018/03/12 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 79.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 450 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 289.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 490 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 81.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 199.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 930 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 75 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1969 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 84 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1969 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 123.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 117.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 645 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 540 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 865 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 122.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 77 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 166.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 47.4 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 70 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 40 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 870 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 890 | ng/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1973 | 2018/02/15 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 75.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 113.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 226.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 80 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1984 | 2018/02/16 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 4300 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1000 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 96.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 103.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 232 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/02/16 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 197 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 111.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >200 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 410 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 94 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 110.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 165 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 158.1 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 190.8 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 730 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 114.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 155.7 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 770 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 363 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 71.2 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 160.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 22.4 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 920 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 12.4 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 78.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 28.9 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 101.5 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 9150 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/12 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 253 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | 2018/03/12 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 20.5 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 57 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2018/02/16 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 840 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 860 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2018/03/11 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 137.2 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 83.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 84.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 35 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1982 | 2018/02/15 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 92.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 136.5 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 513 | μg/L | element | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | 2018/02/16 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 99.6 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 360 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 97.9 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | dissolved | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2018/03/12 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 77.5 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 262.3 | μg/L | element | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2018/03/12 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 120 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S. Hopkins | 1981 | 2018/02/20 | |||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 56 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | 18 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | 60 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S. Hopkins | 1981 | 2018/02/20 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 330 | days | 33 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. | Chronic Toxicity of Copper to Fathead Minnows (Pimphales promelas) | Water Research. | 1968 | 2018/02/16 | ||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | NOEL | 96 | hours | 125 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S. Hopkins | 1981 | 2018/02/20 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | mean number of eggs per female | NOEC | 7 | days | 22.5 | μg/L | total Cu | × | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. | 1977 | 2018/03/08 | |||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 28 | days | 61 | μg/L | mean total copper | × | 12 ECHA Information on Registered Substances | 2 | Scudder, B. et al. | Effects of Copper on Development of the Fathead Minnow, Pimephales promelas | Aquatic Toxicology. | 1988 | 2018/03/08 | |||
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 Fathead Minnows | J. Fish Res. Bd. Canada. | 1969 | 2018/02/16 | ||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 32 | days | 4.8 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 1985 | 2018/03/08 | ||||
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 Fathead Minnows | J. Fish Res. Bd. Canada. | 1969 | 2018/02/16 | ||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 330 | days | 33 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. | Chronic Toxicity of Copper to Fathead Minnows (Pimphales promelas) | Water Research. | 1968 | 2018/02/16 | ||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | embryo development (weight) | NOEC | 32 | days | 57.8 | μg/L | dissoloved | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/03/08 | |||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | mortality | NOEC | 32 | days | 109 | μg/L | dissoloved | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/03/08 | |||||
魚類 | Pimephales promelas (Fathead minnow) | reproduction | NOEC | 330 | days | 14.5 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. | Chronic Toxicity of Copper to Fathead Minnows (Pimphales promelas) | Water Research. | 1968 | 2018/02/16 | ||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | number hatched | NOEC | 7 | days | 109 | μg/L | dissoloved | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/03/08 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 61 | days | 24 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | 2018/02/16 | |||
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 Fathead Minnows | J. Fish Res. Bd. Canada. | 1969 | 2018/02/16 | ||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 61 | days | 45 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | 2018/02/16 | |||
魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 78 | days | 16 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Seim, W.K. et al. | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously or intermittently exposure to copper | Can. J. Fish. Aquat. Sci. | 1984 | 2018/03/08 | ||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | NOEL | 96 | hours | 110 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
魚類 | Lepomis macrochirus (Bluegill) | NOEL | 96 | hours | 36 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
魚類 | Lepomis macrochirus (Bluegill) | NOEL | 96 | hours | <170 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Yamhure | 1981 | 2018/02/20 | |||||||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | NOEL | 96 | hours | >173 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | 1992 | 2018/02/20 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 187 | days | 69.5 | μg/L | total Cu | × | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. | 1977 | 2018/03/08 | |||
魚類 | Pimephales promelas (Fathead minnow) | mean number of eggs per female | NOEC | 187 | days | 25.5 | μg/L | total Cu | × | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. | 1977 | 2018/03/08 | |||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 61 | days | 28 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | 2018/02/16 | |||
魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 60 | days | 2.2 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Marr, J.C.A. et al. | Relationship between copper exposure duration, tissue copper concentration and rainbow trout growth | Aquatic Toxicol. | 1996 | 2018/02/16 | ||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 45 | days | 11.4 | μg/L | dissoloved | × | 12 ECHA Information on Registered Substances | 2 | McKim J.M., J.G. Eaton and G.W. Holcombe | Metal toxicity to embryos and larvae of eight species of freshwater fish - II: copper | 0007-4861/78/0019-0608 Springer-Verlag New York Inc. | 1978 | 2018/03/08 | |||
魚類 | Pimephales promelas (Fathead minnow) | mean number of eggs per female | NOEC | 97 | days | 23 | μg/L | total Cu | × | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. | 1977 | 2018/03/08 | |||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | embryo development (length) | NOEC | 32 | days | 57.8 | μg/L | dissoloved | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2018/03/08 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 45 | days | 11.4 | μg/L | dissoloved | × | 12 ECHA Information on Registered Substances | 2 | McKim J.M., J.G. Eaton and G.W. Holcombe | Metal toxicity to embryos and larvae of eight species of freshwater fish - II: copper | 0007-4861/78/0019-0608 Springer-Verlag New York Inc. | 1978 | 2018/03/08 | |||
魚類 | Pimephales promelas (Fathead minnow) | number of eggs/spawn | NOEC | 270 | days | 66 | μg/L | dissolved | × | 12 ECHA Information on Registered Substances | 2 | Brungs, W.A. et al. | Acute and Chronic Toxicity of Copper to the Fathead Minnow in a Surface Water of Variable Quality | Water Research | 1976 | 2018/03/08 | |||
魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 32 | days | 4.8 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 1985 | 2018/03/08 | ||||
その他 | Juga plicifera | NOEC/L(E)C10 | 6 | μg Cu/L | 4 OECD SIDS (HPVC) | 2019/03/27 |