【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 | Anabaena doliolum | Mortality/Mortality | 15 | days | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | |||||||
藻類 | Pseudokirchneriella subcapitata | Population/Abundance | LC50 LC50 | 96 | hours | 0.54 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Griffitt,R.J., J. Luo, J. Gao, J.C. Bonzongo, and D.S. Barber | Effects of Particle Composition and Species on Toxicity of Metallic Nanomaterials in Aquatic Organisms | Environ. Toxicol. Chem.27(9) | 2008 | ||||||
藻類 | Chlorella vulgaris | Population/Abundance | 4 | days | 9.8 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | |||||||
藻類 | Pseudokirchneriella subcapitata | Population/Abundance | 4 | days | 11.7 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | |||||||
藻類 | Scenedesmus acutus | Population/Abundance | 4 | days | 8.8 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | |||||||
藻類 | Anabaena doliolum | Mortality/Mortality | LC50 LC50 | 15 | days | 10 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 163 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 773 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 65.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.058 | mg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2020/03/03 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 51 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 254 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 440 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 178 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 30 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | EC50 | 72 | hours | 0.058 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of copper copper monochloride to algae (Report No. EG05004), Tested by KRICT | 2005 | 2020/01/28 | ||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 506 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 193 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 102 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | Biomass | EC50 | 72 | hours | 0.057 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of copper copper monochloride to algae (Report No. EG05004), Tested by KRICT | 2005 | 2020/01/28 | ||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 52.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 99 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | Biomass | LOEC | 72 | hours | 0.075 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of copper copper monochloride to algae (Report No. EG05004), Tested by KRICT | 2005 | 2020/01/28 | ||||
藻類 | Pseudokirchneriella subcapitata | Biomass | NOEC | 72 | hours | 0.038 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of copper copper monochloride to algae (Report No. EG05004), Tested by KRICT | 2005 | 2020/01/28 | ||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 99 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 346 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 93 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 194 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 100 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 60 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 296 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 824 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 602 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 380 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 151 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 156 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 84 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 113 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 219 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 811 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 105 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 209 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 205 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 281 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 230 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 35 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 446 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 59 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 462 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 33.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 333 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 174 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 238 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 97.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 245 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 92 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 36.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 199 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 55 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 16.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 35 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 122 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 368 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 685 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 111 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 208 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 756 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 152 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 190 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 364 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 108 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | growth rate | EC50 | 72 | hours | 987 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2006 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 32 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 161 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 268 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2003 | 2020/02/04 | |||||
藻類 | Chlorella vulgaris | Population/Abundance | IC50 IC50 | 4 | days | 61.5 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population/Abundance | IC50 IC50 | 4 | days | 72.5 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Scenedesmus acutus | Population/Abundance | IC50 IC50 | 4 | days | 26.6 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Scenedesmus quadricauda | Population/Abundance | EC50 EC50 | 12 | days | 0.38 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fargasova,A., A. Bumbalova, and E. Havranek | Ecotoxicological Effects and Uptake of Metals (Cu+, Cu2+, Mn2+, Mo6+, Ni2+, V5+) in Freshwater Alga Scenedesmus quadricauda | Chemosphere38(5) | 1999 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 170.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 188 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 188 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | biomass | NOEC | 72 | hours | 164 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | biomass | NOEC | 72 | hours | 61.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 85 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 510 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 0.038 | mg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2020/03/03 | |||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 60.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 91.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | growth rate | LOEC | 72 | hours | 0.075 | mg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 110.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | NOEC | 72 | hours | 0.038 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of copper copper monochloride to algae (Report No. EG05004), Tested by KRICT | 2005 | 2020/01/28 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 59.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | LOEC | 72 | hours | 0.075 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of copper copper monochloride to algae (Report No. EG05004), Tested by KRICT | 2005 | 2020/01/28 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 53.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 37.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 67.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 162 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 112.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 132 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Skeletonema costatum | growth rate | NOEC | 72 | hours | 7.54 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 54.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | biomass | NOEC | 72 | hours | 23.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 49.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | biomass | NOEC | 72 | hours | 52.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 19.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | biomass | NOEC | 72 | hours | 15.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 36 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Phaeodactylum tricornutum | growth rate | EC10 | 72 | hours | 2.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Simpson, S. et al. | Effect of declining toxicant concentrations on algal bioassay endpoints | ; Environmental Toxicology and Chemistry, 22(9) | 2003 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 31 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | biomass | NOEC | 72 | hours | 94.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 111.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 174 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Phaeodactylum tricornutum | growth rate | NOEC | 72 | hours | 5.7 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 99 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 84 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | biomass | NOEC | 72 | hours | 19.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 97.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 63.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 108 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 404 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 159 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 56 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 283 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | biomass | NOEC | 72 | hours | 65.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 89.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 53.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | biomass | NOEC | 72 | hours | 35.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | biomass | NOEC | 72 | hours | 56.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | biomass | NOEC | 72 | hours | 17.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 173 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 40.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Chlorella vulgaris | growth rate | EC10 | 72 | hours | 407 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere, K.C. and Janssen, C.R. | Bioavailability Models for Predicting Copper Toxicity to Freshwater Green Microalgae as a Function of Water Chemistry | Environ. Sci. Technol. 40 | 2006 | ||||
藻類 | biomass | NOEC | 72 | hours | 49 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | NOEC | 72 | hours | 57.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | De Schamphelaere K.A.C., F.M. Vasconcelos, D.G. Heijerick, F.M.G. Tack, K. Delbeke, H.E. Allen, C.R. Janssen | Development and field validation of a predictive copper toxicity model for the green alga Pseudokirchneriella subcapitata | Environmental Toxicology and Chemistry, Vol 22, No. 10 | 2003 | ||||
藻類 | Anabaena doliolum | Physiology/Respiration | LOEC LOEC | 1460 | minutes | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Anabaena doliolum | Population/Population growth rate | LOEC LOEC | 1460 | minutes | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Scenedesmus quadricauda | Population/Abundance | NOEC NOEC | 12 | days | 0.26 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fargasova,A. | Interactive Effect of Manganese, Molybdenum, Nickel, Copper I and II, and Vanadium on the Freshwater Alga Scenedesmus quadricauda | Bull. Environ. Contam. Toxicol.67(5) | 2001 | ||||||
藻類 | Scenedesmus quadricauda | Physiology/Respiratory rate | LOEL LOEL | 12 | days | 0.38 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fargasova,A. | Accumulation and Toxic Effects of Cu2+, Cu+, Mn2+, VO43-, Ni2+ and MoO42- and Their Associations: Influence on Respiratory Rate and Chlorophyll a Content of the Green Alga Scenedesmus quadricauda | J. Trace Microprobe Tech.16(4) | 1998 | ||||||
藻類 | Anabaena doliolum | Physiology/Photosynthesis | LOEC LOEC | 1580 | minutes | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Scenedesmus acutus | Population/Abundance | LOEC LOEC | 4 | days | 10 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Chlorella vulgaris | Population/Abundance | LOEC LOEC | 4 | days | 40 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Scenedesmus acutus | Population/Abundance | NOEC NOEC | 4 | days | <10 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Anabaena doliolum | Physiology/Respiration | LOEC LOEC | 1490 | minutes | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Anabaena doliolum | Population/Population growth rate | LOEC LOEC | 1490 | minutes | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Scenedesmus quadricauda | Population/Chlorophyll A concentration | LOEL LOEL | 12 | days | 0.38 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fargasova,A. | Accumulation and Toxic Effects of Cu2+, Cu+, Mn2+, VO43-, Ni2+ and MoO42- and Their Associations: Influence on Respiratory Rate and Chlorophyll a Content of the Green Alga Scenedesmus quadricauda | J. Trace Microprobe Tech.16(4) | 1998 | ||||||
藻類 | Anabaena doliolum | Physiology/Photosynthesis | NOEC NOEC | 1460 | minutes | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population/Abundance | LOEC LOEC | 4 | days | 40 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Chlorella fusca var. vacuolata | Population/Abundance | LOEC LOEC | 7 | days | 0.0000467 | mol/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sabatini,S.E., A.B. Juarez, M.R. Eppis, L. Bianchi, C.M. Luquet, and M.D.C. Rios de Molina | Oxidative Stress and Antioxidant Defenses in Two Green Microalgae Exposed to Copper | Ecotoxicol. Environ. Saf.72(4) | 2009 | ||||||
藻類 | Anabaena doliolum | Physiology/Photosynthesis | LOEC LOEC | 26 | hours | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Scenedesmus acutus | Population/Abundance | IC10 IC10 | 4 | days | 6.5 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Chlorella fusca var. vacuolata | Population/Abundance | NOEC NOEC | 7 | days | 0.0000342 | mol/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sabatini,S.E., A.B. Juarez, M.R. Eppis, L. Bianchi, C.M. Luquet, and M.D.C. Rios de Molina | Oxidative Stress and Antioxidant Defenses in Two Green Microalgae Exposed to Copper | Ecotoxicol. Environ. Saf.72(4) | 2009 | ||||||
藻類 | Anabaena doliolum | Physiology/Photosynthesis | LOEC LOEC | 1490 | minutes | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Chlorella fusca var. vacuolata | Population/Chlorophyll A:Chlorophyll B | NOEC NOEC | 7 | days | 0.000000000771 | mol/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sabatini,S.E., A.B. Juarez, M.R. Eppis, L. Bianchi, C.M. Luquet, and M.D.C. Rios de Molina | Oxidative Stress and Antioxidant Defenses in Two Green Microalgae Exposed to Copper | Ecotoxicol. Environ. Saf.72(4) | 2009 | ||||||
藻類 | Anabaena doliolum | Population/Population growth rate | LOEC LOEC | 24 | hours | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population/Abundance | NOEC NOEC | 4 | days | 20 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Chlorella vulgaris | Population/Abundance | IC10 IC10 | 4 | days | 6.4 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Chlorella vulgaris | Population/Abundance | NOEC NOEC | 4 | days | 20 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
藻類 | Chlorella fusca var. vacuolata | Population/Chlorophyll A:Chlorophyll B | LOEC LOEC | 7 | days | 0.0000342 | mol/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sabatini,S.E., A.B. Juarez, M.R. Eppis, L. Bianchi, C.M. Luquet, and M.D.C. Rios de Molina | Oxidative Stress and Antioxidant Defenses in Two Green Microalgae Exposed to Copper | Ecotoxicol. Environ. Saf.72(4) | 2009 | ||||||
藻類 | Anabaena doliolum | Physiology/Respiration | LOEC LOEC | 24 | hours | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Anabaena doliolum | Physiology/Photosynthesis | LOEC LOEC | 24 | hours | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
藻類 | Anabaena doliolum | Physiology/Photosynthesis | LOEC LOEC | 1610 | minutes | 20 | μM | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bhargava,P., A. Kumar, Y. Mishra, and L.C. Rai | Copper Pretreatment Augments Ultraviolet B Toxicity in the Cyanobacterium Anabaena doliolum: a Proteomic Analysis of Cell Death | Funct. Plant Biol.35(5) | 2008 | ||||||
甲殻類 | Chironomus riparius | growth | NOEC | 10 | days | 16.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Taylor, E.J. et al. | Evaluation of a Chronic Toxicity Test Using Growth of the Insect Chironomus riparius Meigen | In. Bioindicators and Environmental Management. Eds Jeffrey, D.W. & Madden. Academic Press | 1991 | 2020/03/03 | |||
甲殻類 | Tisbe battagliai | mortality | NOEC | 21 | days | 18 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
甲殻類 | Tisbe battagliai | development | NOEC | 21 | days | 18 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
甲殻類 | Mercenaria mercenaria | development | NOEC | 288 | hours | 7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | LaBreche, T.M.C. et al. | Copper Toxicity to Larval Mercenaria mercenaria (hard clam) | Environ Toxicol Chem., 21 (4) | 2002 | ||||
甲殻類 | Tisbe battagliai | reproduction | NOEC | 21 | days | 18 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | ||||||
甲殻類 | Acanthomysis costata | Growth/Growth, general | NOEC NOEC | 96 | hours | <11 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martin,M., J.W. Hunt, B.S. Anderson, S.L. Turpen, and F.H. Palmer | Experimental Evaluation of the Mysid Holmesimysis costata as a Test Organism for Effluent Toxicity Testing | Environ. Toxicol. Chem.8(11) | 1989 | ||||||
甲殻類 | Acanthomysis costata | Mortality/Mortality | LC50 LC50 | 96 | hours | 17 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martin,M., J.W. Hunt, B.S. Anderson, S.L. Turpen, and F.H. Palmer | Experimental Evaluation of the Mysid Holmesimysis costata as a Test Organism for Effluent Toxicity Testing | Environ. Toxicol. Chem.8(11) | 1989 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 289 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 69 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 66 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 157 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 366 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Dendraster excentricus | development | EC50 | 48 | hours | 14.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 35.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 109 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 136 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 1213 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Dendraster excentricus | development | EC50 | 48 | hours | 28.2 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 792 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Mytilus edulis | Embryo development | NOEC | 48 | hours | 6.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 388 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 210 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | Immobilization | EC100 | 24 | hours | 0.74 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to Daphnia magna (Report No. EG03040), Tested by KRICT | 2003 | 2020/01/28 | ||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 52 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Strongylocentrotus purpuratus | Embryo development | EC50 | 72 | hours | 14.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 14 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 22 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 32 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | Immobilization | EC100 | 48 | hours | 0.74 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to Daphnia magna (Report No. EG03040), Tested by KRICT | 2003 | 2020/01/28 | ||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 36 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 43 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2020/02/26 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 60 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 39 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 27 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 9.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 24 | hours | 0.33 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to Daphnia magna (Report No. EG03040), Tested by KRICT | 2003 | 2020/01/28 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 37.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Dendraster excentricus | Embryo development | EC50 | 48 | hours | 18.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 0.25 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to Daphnia magna (Report No. EG03040), Tested by KRICT | 2003 | 2020/01/28 | ||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 91 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 798 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 56 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 39.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 31 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Strongylocentrotus purpuratus | Embryo development | EC50 | 72 | hours | 24.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Dendraster excentricus | Embryo development | EC50 | 48 | hours | >75.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 826 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 295 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 529 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 63 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Strongylocentrotus purpuratus | Embryo development | EC50 | 72 | hours | 46.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Crassostrea virginica | Embryo development | EC50 | 48 | hours | 40.7 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 10.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 229 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 35 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 244 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 33.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 51 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Dendraster excentricus | development | EC50 | 48 | hours | 6.28 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 119 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 50 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 34 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 40.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 399 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 152 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 106 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 484 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 117 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 70 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 175 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 52 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 46.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 93 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 30 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 44 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 8.5 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 26 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 28.19 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 276 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 76 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 380 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 40 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 421 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 25 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 188 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 58 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 292 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Crassostrea virginica | Embryo development | EC50 | 48 | hours | 30.7 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 300 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Crassostrea virginica | Embryo development | EC50 | 48 | hours | 22.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 47.13 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 465 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 23 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 257 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 92.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Dendraster excentricus | Embryo development | EC50 | 48 | hours | 46.2 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 12.83 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 90 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 9.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/04 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/04 | |||||
甲殻類 | Dendraster excentricus | development | EC50 | 48 | hours | 34.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | ||||
甲殻類 | Crassostrea virginica | Embryo development | EC50 | 48 | hours | 11.2 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 38 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2020/02/26 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 281 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 42 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 526 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 33 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Strongylocentrotus purpuratus | Embryo development | EC50 | 72 | hours | 30.2 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 100 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 46 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1987 | ||||||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 10.89 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 648 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/04 | |||||
甲殻類 | Dendraster excentricus | Embryo development | EC50 | 48 | hours | 36.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | Arnold W. Ray; J.S. Cotsifas, R.S. Ogle, S.G.S. De Palma, D.S. Smith | A comparison of the copper sensitivity of six invertebrate species in ambient salt water of varying dissolved organic matter concentrations. | Env. Tox. and Chem. Vol.29, No2 | 2010 | 2020/02/26 | |||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 10.42 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 31 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Crassostrea gigas | Embryo development | NOEC | 24 | hours | 19.53 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2006 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 686 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 10 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1978 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 37 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 84 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger SC and Cherry DS | Interacting effects of pH acclimation, pH and heaby metals on acute and chronic toxicity to Ceriodaphnia dubia (cladocera) | Journal of Crustacean Biology, 10(2) | 1990 | 2020/02/26 | |||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 332 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2002 | 2020/02/25 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 48 | hours | 0.419 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Griffitt,R.J., J. Luo, J. Gao, J.C. Bonzongo, and D.S. Barber | Effects of Particle Composition and Species on Toxicity of Metallic Nanomaterials in Aquatic Organisms | Environ. Toxicol. Chem.27(9) | 2008 | ||||||
甲殻類 | Crassostrea gigas | Development/Abnormal | EC50 EC50 | 24 | hours | 7.26 | μg/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Brooks,S.J., T. Bolam, L. Tolhurst, J. Bassett, J. La Roche, M. Waldock, J. Barry, and K.V. Thomas | Effects of Dissolved Organic Carbon on the Toxicity of Copper to the Developing Embryos of the Pacific Oyster (Crassostrea gigas) | Environ. Toxicol. Chem.26(8) | 2007 | ||||||
甲殻類 | Crassostrea gigas | Development/Abnormal | EC50 EC50 | 24 | hours | 6.91 | μg/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Brooks,S.J., T. Bolam, L. Tolhurst, J. Bassett, J. La Roche, M. Waldock, J. Barry, and K.V. Thomas | Effects of Dissolved Organic Carbon on the Toxicity of Copper to the Developing Embryos of the Pacific Oyster (Crassostrea gigas) | Environ. Toxicol. Chem.26(8) | 2007 | ||||||
甲殻類 | Crassostrea gigas | Development/Abnormal | EC50 EC50 | 24 | hours | 7.39 | μg/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Brooks,S.J., T. Bolam, L. Tolhurst, J. Bassett, J. La Roche, M. Waldock, J. Barry, and K.V. Thomas | Effects of Dissolved Organic Carbon on the Toxicity of Copper to the Developing Embryos of the Pacific Oyster (Crassostrea gigas) | Environ. Toxicol. Chem.26(8) | 2007 | ||||||
甲殻類 | Crassostrea gigas | Development/Abnormal | EC50 EC50 | 24 | hours | 5.47 | μg/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Brooks,S.J., T. Bolam, L. Tolhurst, J. Bassett, J. La Roche, M. Waldock, J. Barry, and K.V. Thomas | Effects of Dissolved Organic Carbon on the Toxicity of Copper to the Developing Embryos of the Pacific Oyster (Crassostrea gigas) | Environ. Toxicol. Chem.26(8) | 2007 | ||||||
甲殻類 | Acartia tonsa | Mortality/Mortality | 72 | hours | 559 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lussier,S.M., and J.A. Cardin | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | U.S.EPA, Narragansett, RI | 1985 | |||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Mortality | LC50 LC50 | 48 | hours | 0.58 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Griffitt,R.J., J. Luo, J. Gao, J.C. Bonzongo, and D.S. Barber | Effects of Particle Composition and Species on Toxicity of Metallic Nanomaterials in Aquatic Organisms | Environ. Toxicol. Chem.27(9) | 2008 | ||||||
甲殻類 | Daphnia pulex | Mortality/Mortality | LC50 LC50 | 48 | hours | 0.009 | mg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Griffitt,R.J., J. Luo, J. Gao, J.C. Bonzongo, and D.S. Barber | Effects of Particle Composition and Species on Toxicity of Metallic Nanomaterials in Aquatic Organisms | Environ. Toxicol. Chem.27(9) | 2008 | ||||||
甲殻類 | Acartia tonsa | Mortality/Mortality | LC50 LC50 | 72 | hours | 58.1 | ppb | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lussier,S.M., and J.A. Cardin | Results of Acute Toxicity Tests Conducted with Copper at ERL, Narragansett | U.S.EPA, Narragansett, RI | 1985 | ||||||
甲殻類 | Crassostrea gigas | Development/Abnormal | EC50 EC50 | 24 | hours | 8.05 | μg/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Brooks,S.J., T. Bolam, L. Tolhurst, J. Bassett, J. La Roche, M. Waldock, J. Barry, and K.V. Thomas | Effects of Dissolved Organic Carbon on the Toxicity of Copper to the Developing Embryos of the Pacific Oyster (Crassostrea gigas) | Environ. Toxicol. Chem.26(8) | 2007 | ||||||
甲殻類 | Daphnia pulex | Mortality/Mortality | LC50 LC50 | 48 | hours | 0.06 | mg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Griffitt,R.J., J. Luo, J. Gao, J.C. Bonzongo, and D.S. Barber | Effects of Particle Composition and Species on Toxicity of Metallic Nanomaterials in Aquatic Organisms | Environ. Toxicol. Chem.27(9) | 2008 | ||||||
甲殻類 | Crassostrea gigas | Development/Abnormal | EC50 EC50 | 24 | hours | 6.48 | μg/L | Labile | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Brooks,S.J., T. Bolam, L. Tolhurst, J. Bassett, J. La Roche, M. Waldock, J. Barry, and K.V. Thomas | Effects of Dissolved Organic Carbon on the Toxicity of Copper to the Developing Embryos of the Pacific Oyster (Crassostrea gigas) | Environ. Toxicol. Chem.26(8) | 2007 | ||||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 4 | μg/L | measured | × | ○ | 12 ECHA Information on Registered Substances | 2 | Jop, K.M. et al. | Development of a Water-Effect Ratio for Copper, Cadmium and Lead for the Great Works River in Maine Using Ceriodaphnia dubia and Salvelinus fontinalis | Bull. Environ. Contam. Toxicol. 54 | 1995 | 2020/02/25 | ||
甲殻類 | Ceriodaphnia dubia | mortality | NOEC | 7 | days | 19 | μg/L | measured | × | ○ | 12 ECHA Information on Registered Substances | 2 | Jop, K.M. et al. | Development of a Water-Effect Ratio for Copper, Cadmium and Lead for the Great Works River in Maine Using Ceriodaphnia dubia and Salvelinus fontinalis | Bull. Environ. Contam. Toxicol. 54 | 1995 | 2020/02/25 | ||
甲殻類 | Daphnia magna | mortality | LC50 | 21 | days | 0.002 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | WHO | Environmental Health Criteria (EHC) 200, Copper | 1998 | 2020/03/03 | |||||
甲殻類 | Daphnia magna | growth | NOEC | 21 | days | 12.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | van Leeuwen, C.J. et al. | Intermittent Flow System for Population Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol. 40 | 1988 | ||||
甲殻類 | Ceriodaphnia sp. | 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. 93 (3) | 1993 | ||||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 0.007 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | Winner RW et al. | Effect of food type on the acute and chronic toxicity of copper to Daphnia magna | Freshwater Biology 7 | 1985 | 2020/03/03 | ||||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 0.012 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | Winner RW et al. | Effect of food type on the acute and chronic toxicity of copper to Daphnia magna | Freshwater Biology 7 | 1985 | 2020/03/03 | ||||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4) | 1985 | 2020/02/25 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 181 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | ||||||
甲殻類 | Neanthes arenaceodentata | growth | NOEC | 28 | days | 12.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pesch C. E., Schauer, P.S., Balboni, M.A. | Effect of diet on copper toxicity to Neanthes arenaceodentata | NTIS PB 87-167128. pp. 369-383. In: T.M. Poston and R. Purdy (eds.). ASTM Special Technical Publication N°921: Aquatic Toxicology and Environmental Fate, Vol. 9. A Symposium Amer. Soc. Test. Mater. Philadelphia, PA, USA, 530 p. | 1986 | ||||
甲殻類 | Daphnia magna | mortality | NOEC | 21 | days | 36.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | van Leeuwen, C.J. et al. | Intermittent Flow System for Population Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol. 40 | 1988 | ||||
甲殻類 | Ceriodaphnia sp. | mortality | NOEC | 7 | days | 122 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 1985 | 2020/03/03 | |||
甲殻類 | Daphnia magna | mortality | LC50 | 21 | days | 0.001 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | WHO | Environmental Health Criteria (EHC) 200, Copper | 1998 | 2020/03/03 | |||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) | 1990 | 2020/02/25 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 15 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4) | 1985 | 2020/02/25 | |||
甲殻類 | Ceriodaphnia sp. | reproduction | NOEC | 7 | days | 31.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Spehar, R.L. & Fiandt, J.T. | Acute and Chronic Effects of Water Quality Criteria Based Metal Mixtures on Three Aquatic Species | Environmental Research Laboratory, USEPA. Report No. EPA/600/3-85/074 | 1985 | 2020/03/03 | |||
甲殻類 | Neanthes arenaceodentata | growth | NOEC | 28 | days | 13.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pesch C. E., Schauer, P.S., Balboni, M.A. | Effect of diet on copper toxicity to Neanthes arenaceodentata | NTIS PB 87-167128. pp. 369-383. In: T.M. Poston and R. Purdy (eds.). ASTM Special Technical Publication N°921: Aquatic Toxicology and Environmental Fate, Vol. 9. A Symposium Amer. Soc. Test. Mater. Philadelphia, PA, USA, 530 p. | 1986 | ||||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4) | 1985 | 2020/02/25 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 10 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4) | 1985 | 2020/02/25 | |||
甲殻類 | Ceriodaphnia sp. | 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. 93 (3) | 1993 | ||||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4) | 1985 | 2020/02/25 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 0.011 | mg/L | nominal, element | × | ○ | 12 ECHA Information on Registered Substances | 2 | WHO | Environmental Health Criteria (EHC) 200, Copper | 1998 | 2020/03/03 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | NOEC | 7 | days | 4 | μg/L | measured | × | ○ | 12 ECHA Information on Registered Substances | 2 | Jop, K.M. et al. | Development of a Water-Effect Ratio for Copper, Cadmium and Lead for the Great Works River in Maine Using Ceriodaphnia dubia and Salvelinus fontinalis | Bull. Environ. Contam. Toxicol. 54 | 1995 | 2020/02/25 | ||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 24.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. et al. | Effects of Diet, Water Hardness and Population Source on Acute and Chronic Copper Toxicity to Ceriodaphnia dubia | Arch. Environ. Contam. Toxicol. 18 | 1989 | 2020/02/25 | |||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 10 | μg/L | measured | × | ○ | 12 ECHA Information on Registered Substances | 2 | Jop, K.M. et al. | Development of a Water-Effect Ratio for Copper, Cadmium and Lead for the Great Works River in Maine Using Ceriodaphnia dubia and Salvelinus fontinalis | Bull. Environ. Contam. Toxicol. 54 | 1995 | 2020/02/25 | ||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4) | 1985 | 2020/02/25 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 0.017 | mg/L | nominal, CuCl | × | ○ | 12 ECHA Information on Registered Substances | 2 | Biesinger KE, Christensen GM | Effects of various metals on survival, growth, reproduction, and metabolism of Daphnia magna | J Fish Res Board Can 29(12) | 1972 | 2020/03/04 | ||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 0 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | WHO | Environmental Health Criteria (EHC) 200, Copper | 1998 | 2020/03/03 | |||||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 0.005 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | Winner RW et al. | Effect of food type on the acute and chronic toxicity of copper to Daphnia magna | Freshwater Biology 7 | 1985 | 2020/03/03 | ||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 71.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | ||||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 21.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | ||||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 6.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. et al. | Effects of Diet, Water Hardness and Population Source on Acute and Chronic Copper Toxicity to Ceriodaphnia dubia | Arch. Environ. Contam. Toxicol. 18 | 1989 | 2020/02/25 | |||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) | 1990 | 2020/02/25 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4) | 1985 | 2020/02/25 | |||
甲殻類 | Daphnia magna | population growth | NOEC | 21 | days | 36.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | van Leeuwen, C.J. et al. | Intermittent Flow System for Population Studies Demonstrated with Daphnia and Copper | Bull. Environ. Contam. Toxicol. 40 | 1988 | ||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 10 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) | 1990 | 2020/02/25 | |||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 20 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Belanger, S.E. & Cherry, D.S. | Interacting Effects of pH Acclimation, pH and Heavy Metals on Acute and Chronic Toxicity to Ceriodaphnia dubia (Cladocera) | J. Crustacean Biology. 10 (2) | 1990 | 2020/02/25 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 0 | mg/L | nominal, element | × | 12 ECHA Information on Registered Substances | 2 | Dave G | Effects of copper on growth, reproduction, survival and haemoglobin in Daphnia magna | Comp Biochem Physiol, 78C(2) | 1984 | 2020/03/03 | |||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 106 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | ||||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 68.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2001 | ||||||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 30 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4) | 1985 | 2020/02/25 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 40 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Winner, R.W. | Bioaccumulation and toxicity of copper as affected by interactions between humic acid and water hardness | Water Research 19(4) | 1985 | 2020/02/25 | |||
甲殻類 | Daphnia pulex | mortality | NOEC | 42 | days | 0.008 | mg/L | meas. (not specified), test mat. | ○ | 12 ECHA Information on Registered Substances | 2 | U.S. EPA | Aquatic life ambient freshwater quality criteria – Copper, 2007 Revision | EPA-822-R-07-001, Feb 2007 | 2007 | 2020/03/03 | |||
甲殻類 | Ceriodaphnia dubia | Reproduction/ Progeny counts/numbers | NOEC NOEC | 7 | days | 5 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
甲殻類 | Ceriodaphnia dubia | Feeding behavior/Food consumption | NOEC NOEC | 7 | days | 40 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Survival | EC50 EC50 | 7 | days | 54.4 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
甲殻類 | Ceriodaphnia dubia | Reproduction/ Progeny counts/numbers | LOEC LOEC | 7 | days | 10 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Survival | LOEC LOEC | 7 | days | 20 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
甲殻類 | Ceriodaphnia dubia | Feeding behavior/Food consumption | LOEC LOEC | 7 | days | 80 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality/Survival | NOEC NOEC | 7 | days | 10 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
甲殻類 | Ceriodaphnia dubia | Reproduction/ Progeny counts/numbers | IC50 IC50 | 7 | days | 41.6 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sofyan,A. | Toxicity of Metals to Green Algae and Ceriodaphnia dubia: The Importance of Water Column and Dietary Exposures | Ph.D.Thesis, University of Kentucky, Lexington, KY | 2004 | ||||||
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 | 2020/03/04 | |||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | embryo development (weight) | NOEC | 32 | days | 57.8 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2020/03/04 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 11 | months | 0.016 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | Mount DI | Chronic toxicity of copper to fathead minnow (Pimephales promelas) in soft water | J Fish Res Board Can 26 | 1969 | 2020/03/04 | ||||
魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 11 | months | 0.016 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | Mount DI | Chronic toxicity of copper to fathead minnow (Pimephales promelas) in soft water | J Fish Res Board Can 26 | 1969 | 2020/03/04 | ||||
魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 11 | months | 0.01 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | Mount DI | Chronic toxicity of copper to fathead minnow (Pimephales promelas) in soft water | J Fish Res Board Can 26 | 1969 | 2020/03/04 | ||||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | mortality | NOEC | 32 | days | 109 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2020/03/04 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 327 | days | 10.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. & Stephan, C.E. | Chronic Toxicity of Copper to the Fathead Minnow | J. Fish Res. Bd. Canada. 26 | 1969 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | reproduction | NOEC | 330 | days | 14.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. | Chronic Toxicity of Copper to Fathead Minnows (Pimphales promelas) | Water Research. 2 | 1968 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 330 | days | 33 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. | Chronic Toxicity of Copper to Fathead Minnows (Pimphales promelas) | Water Research. 2 | 1968 | 2020/03/04 | |||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | embryo development (length) | NOEC | 32 | days | 57.8 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2020/03/04 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | biomass | NOEC | 84 | days | 0.042 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | U.S. EPA | Aquatic life ambient freshwater quality criteria – Copper, 2007 Revision | EPA-822-R-07-001, Feb 2007 | 2007 | 2020/03/04 | ||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | biomass | EC20 | 84 | days | 0.028 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | Seim WK et al. | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously or intermittently exposed to copper. | Can J Fish Aquat Sci 41(3) | 1984 | 2020/03/04 | ||||
魚類 | Pimephales promelas (Fathead minnow) | reproduction | NOELR | 11 | months | 0.01 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | Mount DI | Chronic toxicity of copper to fathead minnow (Pimephales promelas) in soft water | J Fish Res Board Can 26 | 1969 | 2020/03/04 | ||||
魚類 | Pimephales promelas (Fathead minnow) | reproduction | NOEC | 327 | days | 10.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. & Stephan, C.E. | Chronic Toxicity of Copper to the Fathead Minnow | J. Fish Res. Bd. Canada. 26 | 1969 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 327 | days | 10.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. & Stephan, C.E. | Chronic Toxicity of Copper to the Fathead Minnow | J. Fish Res. Bd. Canada. 26 | 1969 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | mean number of eggs per female | NOEC | 7 | days | 22.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11 | 1977 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | mean number of eggs per female | NOEC | 187 | days | 25.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11 | 1977 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 187 | days | 69.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11 | 1977 | 2020/03/04 | |||
魚類 | Oncorhynchus mykiss (Rainbow trout) | biomass | EC20 | 84 | days | 0.043 | mg/L | meas. (not specified), test mat. | ○ | 12 ECHA Information on Registered Substances | 1 | Seim WK et al. | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously or intermittently exposed to copper. | Can J Fish Aquat Sci 41(3) | 1984 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 11 | months | 0.01 | mg/L | meas. (not specified), element | ○ | 12 ECHA Information on Registered Substances | 1 | WHO | Environmental Health Criteria (EHC) 200, Copper | ISBN 9241572000 | 1998 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | growth rate | NOEC | 330 | days | 33 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mount, D.I. | Chronic Toxicity of Copper to Fathead Minnows (Pimphales promelas) | Water Research. 2 | 1968 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | mean number of eggs per female | NOEC | 97 | days | 23 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Pickering, Q. et al. | Effect of Exposure, Time and Copper Concentration on Reproduction of the Fathead Minnow (Pimephales promelas) | Water Res. 11 | 1977 | 2020/03/04 | |||
魚類 | Cyprinodon variegatus (Sheepshead minnow) | number hatched | NOEC | 7 | days | 109 | μg/L | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2020/03/04 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 78 | days | 16 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Seim, W.K. et al. | Growth and survival of developing steelhead trout (Salmo gairdneri) continuously or intermittently exposure to copper | Can. J. Fish. Aquat. Sci. Vol. 41 | 1984 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 28 | days | 61 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Scudder, B. et al. | Effects of Copper on Development of the Fathead Minnow, Pimephales promelas | Aquatic Toxicology. 12 | 1988 | 2020/03/04 | |||
魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 60 | days | 2.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Marr, J.C.A. et al. | Relationship between copper exposure duration, tissue copper concentration and rainbow trout growth | Aquatic Toxicol. 36 | 1996 | 2020/03/04 | |||
魚類 | Oncorhynchus mykiss (Rainbow trout) | biomass | NOEC | 84 | days | 0.023 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | U.S. EPA | Aquatic life ambient freshwater quality criteria – Copper, 2007 Revision | EPA-822-R-07-001, Feb 2007 | 2007 | 2020/03/04 | ||||
魚類 | Pimephales promelas (Fathead minnow) | reproduction | NOELR | 11 | months | 0.016 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | WHO | Environmental Health Criteria (EHC) 200, Copper | ISBN 9241572000 | 1998 | 2020/03/04 | ||||
魚類 | Pimephales promelas (Fathead minnow) | number of eggs/spawn | NOEC | 270 | days | 66 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Brungs, W.A. et al. | Acute and Chronic Toxicity of Copper to the Fathead Minnow in a Surface Water of Variable Quality | Water Research. 10 | 1976 | 2020/03/04 | |||
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 | 2020/03/04 | |||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 58.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 164 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 960 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 0.015 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Marr JCA, Hansen JA, Meyer JS, Cacela D, Podrabsky T, Lipton J, Bergman HL | Toxicity of cobalt and copper to rainbow trout: application of a mechanistic model for predicting survival | Aquat Toxicol 43 | 1998 | |||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 103 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 84 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1969 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC20 | 0.016 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Marr JCA, Hansen JA, Meyer JS, Cacela D, Podrabsky T, Lipton J, Bergman HL | Toxicity of cobalt and copper to rainbow trout: application of a mechanistic model for predicting survival | Aquat Toxicol 43 | 1998 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 210 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 126.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 243 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 865 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 221 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 92.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 514 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 75.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >780 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 0.023 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Marr JCA, Hansen JA, Meyer JS, Cacela D, Podrabsky T, Lipton J, Bergman HL | Toxicity of cobalt and copper to rainbow trout: application of a mechanistic model for predicting survival | Aquat Toxicol 43 | 1998 | |||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 40 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 758.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 660 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 103.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 450 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 253 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 79.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 96 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 516 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 110.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >800 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 650 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 150.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 2.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2020/02/25 | |||||
魚類 | Cyprinus carpio (Carp) | mortality | LC50 | 96 | hours | 800 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 646.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 953 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 19.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 22.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 30 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1090 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 148.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | <640 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 78.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 940.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 650 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 137.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 190.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 36.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 4250 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 4300 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 28.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Cyprinus carpio (Carp) | mortality | LC50 | 96 | hours | 810 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1971 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 83.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 81.1 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 297 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 289.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 117.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 730 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/04 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 17.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 360 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1400 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 193 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 298 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 9150 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 47.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC0 | 24 | hours | 0.047 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 465 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | >89 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 311 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | NOEC | 24 | hours | 0.033 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC100 | 72 | hours | 0.047 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC0 | 48 | hours | 0.033 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC0 | 72 | hours | 0.021 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 72 | hours | 0.039 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 10.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 31.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC0 | 96 | hours | 0.021 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC100 | 48 | hours | 0.047 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | NOEC | 48 | hours | 0.033 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | NOEC | 96 | hours | 0.021 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | NOEC | 72 | hours | 0.021 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 870 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/04 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 75 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1969 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 12.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 48 | hours | 0.044 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 96 | hours | 0.039 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 24 | hours | 0.16 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1000 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 199.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC100 | 96 | hours | 0.047 | mg/L | ○ | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | The acute toxicity of copper monochloride to fish (Report No. EG05003), Tested by KRICT | 2005 | 2020/01/28 | ||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 410 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2020/02/25 | |||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 149 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 630 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/04 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/04 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 165 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >810 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 930 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/03 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 102 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 42.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 131.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 830 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/03 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 18 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 810 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 20.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 1000 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1980 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 158.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 680 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 645 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 230 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 44.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 38.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >830 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 950 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 132.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 229.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 52 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 920 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 210 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/01/31 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 286 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1983 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 698 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 690 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 653.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 242.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 253.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 82.2 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 125.7 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 182.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 26.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 101.5 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 181 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 176.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 226.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 750 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 690 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 970 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 890 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1973 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 191.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 128 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 390 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 980 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 171 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 490 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 71.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 167.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 94 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 122.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 125.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 160.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 663 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 21 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 84.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 274 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 18.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 80 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1984 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 111.8 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 123.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 292.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 168.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 15 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/01/31 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 309 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 1100 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1975 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 77 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 21.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >800 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 580 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC20 | 0.013 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Marr JCA, Hansen JA, Meyer JS, Cacela D, Podrabsky T, Lipton J, Bergman HL | Toxicity of cobalt and copper to rainbow trout: application of a mechanistic model for predicting survival | Aquat Toxicol 43 | 1998 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 268.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 70 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | 2020/02/25 | |||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 770 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1954 | ||||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 35 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1982 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 780 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 29 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 223.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 70.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 94 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 190.8 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 9.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 18 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1998 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 760 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 460 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 430 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1968 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 640 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 17 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 4.2 | μg/L | meas.(not specified), element | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1986 | 2020/02/25 | ||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 166.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 28 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 183 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 85.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 113.4 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 112 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 600 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 169 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 710 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1954 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 152 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 46.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/03 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 190 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 940 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC20 | 0.01 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Marr JCA, Hansen JA, Meyer JS, Cacela D, Podrabsky T, Lipton J, Bergman HL | Toxicity of cobalt and copper to rainbow trout: application of a mechanistic model for predicting survival | Aquat Toxicol 43 | 1998 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 1060 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 151 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 232 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 920 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 540 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 127.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 644.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 16.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 68.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 427 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 96.7 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 155.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 820 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 5.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 256.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 35 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 289.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 200 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 521 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 600 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/03 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 175.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 62.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 44 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/01/31 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 83.3 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 0.018 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Marr JCA, Hansen JA, Meyer JS, Cacela D, Podrabsky T, Lipton J, Bergman HL | Toxicity of cobalt and copper to rainbow trout: application of a mechanistic model for predicting survival | Aquat Toxicol 43 | 1998 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 370.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 405.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 143 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 197 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 57 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1978 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 41.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 21.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 490 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 12.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1999 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 97.9 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 840 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/04 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 271.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 129.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 68 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 470 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1968 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 42.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 20.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 513 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1995 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 23.2 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 262.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 390 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1981 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 770 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/04 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 122.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 4.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 860 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1976 | 2020/03/04 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >610 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 172.6 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 93 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 1993 | 2020/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 189.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 77.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 52.7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 283.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 752.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 81.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 62.5 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 363 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | <=560 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 830 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1976 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 996.3 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 496 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 136.5 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | publication | 1979 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 99.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 114.6 | μg/L | × | × | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 12.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 905.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | >449 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 892.1 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1996 | 2020/02/25 | |||||
魚類 | Fundulus heteroclitus (Mummichog) | Mortality/Mortality | LC50 LC50/ | 24 | hours | 2300 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | ||||||
魚類 | Fundulus heteroclitus (Mummichog) | Mortality/Mortality | LC50 LC50/ | 72 | hours | 2300 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality/Mortality | LC50 LC50 | 48 | hours | 0.71 | mg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Griffitt,R.J., J. Luo, J. Gao, J.C. Bonzongo, and D.S. Barber | Effects of Particle Composition and Species on Toxicity of Metallic Nanomaterials in Aquatic Organisms | Environ. Toxicol. Chem.27(9) | 2008 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality/Mortality | LC50 LC50 | 48 | hours | 1.78 | mg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Griffitt,R.J., J. Luo, J. Gao, J.C. Bonzongo, and D.S. Barber | Effects of Particle Composition and Species on Toxicity of Metallic Nanomaterials in Aquatic Organisms | Environ. Toxicol. Chem.27(9) | 2008 | ||||||
魚類 | Fundulus heteroclitus (Mummichog) | Mortality/Mortality | LC50 LC50/ | 96 | hours | 2300 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality/Mortality | LC50 LC50 | 48 | hours | 0.94 | mg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Griffitt,R.J., J. Luo, J. Gao, J.C. Bonzongo, and D.S. Barber | Effects of Particle Composition and Species on Toxicity of Metallic Nanomaterials in Aquatic Organisms | Environ. Toxicol. Chem.27(9) | 2008 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.0905 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Fundulus heteroclitus (Mummichog) | Mortality/Mortality | LC50 LC50/ | 24 | hours | 1700 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.559 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.183 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.297 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.264 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.0627 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.24 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality/Mortality | LC50 LC50 | 48 | hours | 0.13 | mg/L | Dissolved | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Griffitt,R.J., J. Luo, J. Gao, J.C. Bonzongo, and D.S. Barber | Effects of Particle Composition and Species on Toxicity of Metallic Nanomaterials in Aquatic Organisms | Environ. Toxicol. Chem.27(9) | 2008 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.214 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Fundulus heteroclitus (Mummichog) | Mortality/Mortality | LC50 LC50/ | 48 | hours | 500 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | ||||||
魚類 | Fundulus heteroclitus (Mummichog) | Mortality/Mortality | LC50 LC50/ | 72 | hours | 400 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | ||||||
魚類 | Fundulus heteroclitus (Mummichog) | Mortality/Mortality | LC50 LC50/ | 48 | hours | 2300 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | ||||||
魚類 | Fundulus heteroclitus (Mummichog) | Mortality/Mortality | LC50 LC50/ | 96 | hours | 400 | μg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.0723 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.139 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality/Mortality | LC50 LC50 | 96 | hours | 0.179 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Chakoumakos,C. | The Toxicity of Copper to Rainbow and Cutthroat Trouts Under Different Conditions of Alkalinity, pH, and Hardness | M.S.Thesis, University of Wisconsin, Madison, WI | 1977 | ||||||
mortality | NOEC | 72 | hours | 21 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Sauter, S. et al. | Effects of exposure to heavy metals on selected freshwater fish. Toxicity of copper, cadmium, chromium and lead to eggs and fry of seven fish species. | Ecological Research Series EPA-600/3-76-105. U.S. Environmental Protection Agency, Environmental Research Laboratory, Duluth, Minnesota | 1976 | ||||||
growth rate | NOEC | 327 | days | 13 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Sauter, S. et al. | Effects of exposure to heavy metals on selected freshwater fish. Toxicity of copper, cadmium, chromium and lead to eggs and fry of seven fish species. | Ecological Research Series EPA-600/3-76-105. U.S. Environmental Protection Agency, Environmental Research Laboratory, Duluth, Minnesota | 1976 | ||||||
larval development | EC50 | 48 | hours | 3.52~4.66 | μg/L | × | × | 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 | ||||||
larval development | EC50 | 48 | hours | 8.03~9.9 | μg/L | × | × | 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 | ||||||
mortality | NOEC | 46 | days | 9.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Young, J.S., Gurtisen, J.M., Apts, C.W., Crecelius, E.A. | The Relationship Between the Copper Complexing Capacity of Sea Water and Copper Toxicity in Shrimp Zoeae | Mar. Environ. Res. 2 | 1979 | ||||||
mortality | NOEC | 32 | days | 11.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | McKim J.M., J.G. Eaton and G.W. Holcombe | Metal toxicity to embryos and larvae of eight species of freshwater fish - II: copper | 0007-4861/78/0019-0608 Springer-Verlag New York Inc. | 1978 | ||||||
growth rate | NOEC | 72 | hours | 7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Sauter, S. et al. | Effects of exposure to heavy metals on selected freshwater fish. Toxicity of copper, cadmium, chromium and lead to eggs and fry of seven fish species. | Ecological Research Series EPA-600/3-76-105. U.S. Environmental Protection Agency, Environmental Research Laboratory, Duluth, Minnesota | 1976 | ||||||
larval development | EC50 | 48 | hours | 21.6~25.2 | μg/L | × | × | 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 | ||||||
growth rate | NOEC | 30 | days | 11.4 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | McKim J.M., J.G. Eaton and G.W. Holcombe | Metal toxicity to embryos and larvae of eight species of freshwater fish - II: copper | 0007-4861/78/0019-0608 Springer-Verlag New York Inc. | 1978 | ||||||
mortality | NOEC | 42 | days | 13 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Sauter, S. et al. | Effects of exposure to heavy metals on selected freshwater fish. Toxicity of copper, cadmium, chromium and lead to eggs and fry of seven fish species. | Ecological Research Series EPA-600/3-76-105. U.S. Environmental Protection Agency, Environmental Research Laboratory, Duluth, Minnesota | 1976 | ||||||
mortality | NOEC | 64 | days | 28 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | In: Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | ||||||
reproduction | NOEC | 42 | days | 49 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Sauter, S. et al. | Effects of exposure to heavy metals on selected freshwater fish. Toxicity of copper, cadmium, chromium and lead to eggs and fry of seven fish species. | Ecological Research Series EPA-600/3-76-105. U.S. Environmental Protection Agency, Environmental Research Laboratory, Duluth, Minnesota | 1976 | ||||||
reproduction | NOEC | 42 | days | 7 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Sauter, S. et al. | Effects of exposure to heavy metals on selected freshwater fish. Toxicity of copper, cadmium, chromium and lead to eggs and fry of seven fish species. | Ecological Research Series EPA-600/3-76-105. U.S. Environmental Protection Agency, Environmental Research Laboratory, Duluth, Minnesota | 1976 | ||||||
mortality | LC50 | 96 | hours | 108 | μg/L | × | 12 ECHA Information on Registered Substances | 2 | Hall L.W., R.D. Anderson, B.L. Lewis, W.R. Arnold | The influence of salinity and dissolved organic carbon on the toxicity of copper to the estuarine copepod, Eurytemora affinis | Arch Environ Contam Toxicol 54 | 2008 | |||||||
development | NOEC | 46 | days | 9.9 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Young, J.S., Gurtisen, J.M., Apts, C.W., Crecelius, E.A. | The Relationship Between the Copper Complexing Capacity of Sea Water and Copper Toxicity in Shrimp Zoeae | Mar. Environ. Res. 2 | 1979 | ||||||
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, 65(2) | 1985 | ||||||
larval development | EC50 | 48 | hours | 14~17.5 | μg/L | × | × | 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 | ||||||
mortality | NOEC | 12 | days | 24 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | In: Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | ||||||
growth rate | NOEC | 12 | days | 45 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Mudge, J.E. et al. | Effects of Varying Environmental Conditions on the Toxicity of Copper to Salmon | In: Environmental Toxicology and Risk Assessment: 2nd Volume, STP 121, Eds. Gorsuch, J.W. et al. American Society for Testing Materials, Philadelphia 1993 | 1993 | ||||||
mortality | NOEC | 72 | hours | 13 | μg/L | × | ○ | 12 ECHA Information on Registered Substances | 2 | Sauter, S. et al. | Effects of exposure to heavy metals on selected freshwater fish. Toxicity of copper, cadmium, chromium and lead to eggs and fry of seven fish species. | Ecological Research Series EPA-600/3-76-105. U.S. Environmental Protection Agency, Environmental Research Laboratory, Duluth, Minnesota | 1976 |