【注意事項】
* 生態影響に係る有害性情報更新日が2019年9月以前はRead-acrossデータに○を記載しておらず、被験物質が標記の物質ではない可能性がある。
**各情報源における信頼性評価スコアの定義は下記のとおりである。
生物種 | 学名 | 影響内容 | エンドポイント | 暴露期間(値) | 暴露期間(単位) | 毒性値 | 毒性値(単位) | 毒性値(単位)種別 | 試験中の 被験物質 濃度測定 あり:○ なし:× |
情報源 | 情報源による 信頼性評価** |
著者 | タイトル | 記載誌 | 発行年 | 情報更新日 | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
subject type | scientific name | effect | endpoint | exposure duration value |
exposure duration unit |
toxicity value | toxicity unit | toxicity unit type | Read-across* | QSAR | GLP | measurement of the test material |
original work type | original work reliability rank |
author | title | referenced journal | publication year | Information update date |
藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 3 | days | 4.7 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2018/03/02 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 3 | days | 0.53 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Yang,L.H., G.G. Ying, H.C. Su, J.L. Stauber, M.S. Adams, and M.T. Binet | Growth-Inhibiting Effects of 12 Antibacterial Agents and Their Mixtures on the Freshwater Microalga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.27(5): 1201-1208 | 2008 | 2018/03/02 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | LOEC | 3 | days | 0.4 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Yang,L.H., G.G. Ying, H.C. Su, J.L. Stauber, M.S. Adams, and M.T. Binet | Growth-Inhibiting Effects of 12 Antibacterial Agents and Their Mixtures on the Freshwater Microalga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.27(5): 1201-1208 | 2008 | 2018/03/02 | |||||
藻類 | Anabaena flos-aquae | Population | NOEL | 4 | days | <0.5 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/02 | |||||
藻類 | Navicula pelliculosa | Population | NOEL | 4 | days | <0.5 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/02 | |||||
藻類 | Anabaena flos-aquae | Population | EC50 | 4 | days | 1.2 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/02 | |||||
藻類 | Scenedesmus subspicatus | Population | LOEC | 3 | days | 1.2 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/19 | |||||
藻類 | Anabaena flos-aquae | Population | EC50 | 4 | days | 0.97 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
藻類 | Scenedesmus subspicatus | Population | EC50 | 4 | days | 0.7 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | NOEL | 4 | days | 2.5 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/02 | |||||
藻類 | Scenedesmus subspicatus | Population | EC50 | 3 | days | 120 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/19 | |||||
藻類 | Navicula pelliculosa | Population | EC50 | 4 | days | 16 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/02 | |||||
藻類 | Scenedesmus subspicatus | Population | EC50 | 3 | days | 2.8 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/19 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 3.4 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/02 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 3 | days | 0.2 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Yang,L.H., G.G. Ying, H.C. Su, J.L. Stauber, M.S. Adams, and M.T. Binet | Growth-Inhibiting Effects of 12 Antibacterial Agents and Their Mixtures on the Freshwater Microalga Pseudokirchneriella subcapitata | Environ. Toxicol. Chem.27(5): 1201-1208 | 2008 | 2018/03/02 | |||||
藻類 | Navicula pelliculosa | Population | EC50 | 4 | days | 19.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
藻類 | Navicula pelliculosa | Population | EC25 | 4 | days | 10.7 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2016/03/25 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population | IC25 | 3 | days | 3.4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2016/03/25 | ||||||
藻類 | Skeletonema costatum | Population | NOEL | 4 | days | <12.6 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/19 | |||||
藻類 | Chlorella sp. Chlorella fusca var. vacuolata | Population | EC50 | 0.75 | days | 5.08 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vogs,C., N. Bandow, and R. Altenburger | Effect Propagation in a Toxicokinetic/Toxicodynamic Model Explains Delayed Effects on the Growth of Unicellular Green Algae Scenedesmus vacuolatus | Environ. Toxicol. Chem.32(5): 1161-1172 | 2013 | 2018/03/19 | |||||
藻類 | Chlorella sp. Chlorella fusca var. vacuolata | Population | EC50 | 0.67 | days | 5.83 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vogs,C., N. Bandow, and R. Altenburger | Effect Propagation in a Toxicokinetic/Toxicodynamic Model Explains Delayed Effects on the Growth of Unicellular Green Algae Scenedesmus vacuolatus | Environ. Toxicol. Chem.32(5): 1161-1172 | 2013 | 2018/03/19 | |||||
藻類 | Chlorella sp. Chlorella fusca var. vacuolata | Population | EC50 | 0.83 | days | 5.71 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vogs,C., N. Bandow, and R. Altenburger | Effect Propagation in a Toxicokinetic/Toxicodynamic Model Explains Delayed Effects on the Growth of Unicellular Green Algae Scenedesmus vacuolatus | Environ. Toxicol. Chem.32(5): 1161-1172 | 2013 | 2018/03/19 | |||||
藻類 | Chlorella sp. Chlorella fusca var. vacuolata | Population | EC50 | 0.42 | days | 9.13 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vogs,C., N. Bandow, and R. Altenburger | Effect Propagation in a Toxicokinetic/Toxicodynamic Model Explains Delayed Effects on the Growth of Unicellular Green Algae Scenedesmus vacuolatus | Environ. Toxicol. Chem.32(5): 1161-1172 | 2013 | 2018/03/19 | |||||
藻類 | Chlorella sp. Chlorella fusca var. vacuolata | Population | EC50 | 0.33 | days | 14.77 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vogs,C., N. Bandow, and R. Altenburger | Effect Propagation in a Toxicokinetic/Toxicodynamic Model Explains Delayed Effects on the Growth of Unicellular Green Algae Scenedesmus vacuolatus | Environ. Toxicol. Chem.32(5): 1161-1172 | 2013 | 2018/03/19 | |||||
藻類 | Skeletonema costatum | Population | EC50 | 4 | days | >66 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/19 | |||||
藻類 | Skeletonema costatum | Population | EC50 | 4 | days | >66 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/19 | |||||
藻類 | Chlorella sp. Chlorella fusca var. vacuolata | Population | EC50 | 1 | days | 2.85 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vogs,C., N. Bandow, and R. Altenburger | Effect Propagation in a Toxicokinetic/Toxicodynamic Model Explains Delayed Effects on the Growth of Unicellular Green Algae Scenedesmus vacuolatus | Environ. Toxicol. Chem.32(5): 1161-1172 | 2013 | 2018/03/19 | |||||
藻類 | Chlorella sp. Chlorella fusca var. vacuolata | Population | EC50 | 0.92 | days | 12.5 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vogs,C., N. Bandow, and R. Altenburger | Effect Propagation in a Toxicokinetic/Toxicodynamic Model Explains Delayed Effects on the Growth of Unicellular Green Algae Scenedesmus vacuolatus | Environ. Toxicol. Chem.32(5): 1161-1172 | 2013 | 2018/03/19 | |||||
藻類 | Dunaliella tertiolecta | Population | LOEC | 4 | days | 4.9 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | DeLorenzo,M.E., and J. Fleming | Individual and Mixture Effects of Selected Pharmaceuticals and Personal Care Products on the Marine Phytoplankton Species Dunaliella tertiolecta | Arch. Environ. Contam. Toxicol.54(2): 203-210 | 2008 | 2018/03/19 | |||||
藻類 | Dunaliella tertiolecta | Population | EC50 | 4 | days | 3.55 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | DeLorenzo,M.E., and J. Fleming | Individual and Mixture Effects of Selected Pharmaceuticals and Personal Care Products on the Marine Phytoplankton Species Dunaliella tertiolecta | Arch. Environ. Contam. Toxicol.54(2): 203-210 | 2008 | 2018/03/19 | |||||
藻類 | Dunaliella tertiolecta | Population | NOEC | 4 | days | 1.6 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | DeLorenzo,M.E., and J. Fleming | Individual and Mixture Effects of Selected Pharmaceuticals and Personal Care Products on the Marine Phytoplankton Species Dunaliella tertiolecta | Arch. Environ. Contam. Toxicol.54(2): 203-210 | 2008 | 2018/03/19 | |||||
藻類 | Chlorella sp. Chlorella fusca var. vacuolata | Population | EC50 | 0.5 | days | 5.16 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vogs,C., N. Bandow, and R. Altenburger | Effect Propagation in a Toxicokinetic/Toxicodynamic Model Explains Delayed Effects on the Growth of Unicellular Green Algae Scenedesmus vacuolatus | Environ. Toxicol. Chem.32(5): 1161-1172 | 2013 | 2018/03/19 | |||||
藻類 | Chlorella sp. Chlorella fusca var. vacuolata | Population | EC50 | 0.58 | days | 6.6 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vogs,C., N. Bandow, and R. Altenburger | Effect Propagation in a Toxicokinetic/Toxicodynamic Model Explains Delayed Effects on the Growth of Unicellular Green Algae Scenedesmus vacuolatus | Environ. Toxicol. Chem.32(5): 1161-1172 | 2013 | 2018/03/19 | |||||
藻類 | Scenedesmus subspicatus | Population | LOEC | 4 | days | 1.2 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
藻類 | Scenedesmus subspicatus | Population | NOEL | 3 | days | 40 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/19 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 4.46 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
藻類 | Scenedesmus subspicatus | Population | NOEC | 4 | days | 0.5 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
藻類 | Scenedesmus subspicatus | Population | NOEC | 3 | days | 0.5 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/19 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | EC25 | 4 | days | 2.44 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2016/03/25 | ||||||
藻類 | Anabaena flos-aquae | Population | EC25 | 4 | days | 0.67 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2016/03/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 96 | hours | 4.6 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC50 | 96 | hours | 1.6 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 96 | hours | 13.7 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 72 | hours | 2.8 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1995 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC50 | 72 | hours | 1.4 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 96 | hours | 1.61 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 72 | hours | 0.17 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC50 | 96 | hours | 3.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 96 | hours | 4.46 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Navicula pelliculosa | growth rate | EC50 | 96 | hours | 0.44 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC50 | 72 | hours | 0.7 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1995 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 96 | hours | 2.25 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Navicula pelliculosa | biomass | EC50 | 96 | hours | 19.1 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Skeletonema costatum | growth inhibition | EC50 | 96 | hours | >66 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 21-02-1 | 1997 | 2018/02/07 | ||||||
藻類 | Desmodesmus subspicatus | growth inhibition | EC50 | 72 | hours | 1.89 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 43118 | 1997 | 2018/02/07 | ||||||
藻類 | Desmodesmus subspicatus | growth inhibition | EC50 | 72 | hours | 0.17 | μg/L | 12 ECHA Information on Registered Substances | 1 | Ciba Specialty Chem. | Rep. No.A34918 | 2006 | 2018/02/07 | ||||||
藻類 | Navicula pelliculosa | growth inhibition | EC50 | 96 | hours | 55.96 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 21-02-1 | 1997 | 2018/02/07 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth inhibition | EC50 | 72 | hours | 5.1 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tamura et al. | 2012 | 2018/02/07 | |||||||
藻類 | Pseudokirchneriella subcapitata | growth inhibition | EC50 | 96 | hours | 15.84 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 21-02-1 | 1997 | 2018/02/07 | ||||||
藻類 | Anabaena flos-aquae | growth inhibition | EC50 | 96 | hours | 1.08 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 21-02-1 | 1997 | 2018/02/07 | ||||||
藻類 | Desmodesmus subspicatus | growth inhibition | EC50 | 72 | hours | 1.99 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba Specialty Chemicals | Rep. No. 385837 | 1995 | 2018/02/07 | ||||||
藻類 | Anabaena flos-aquae | growth inhibition | EC50 | 72 | hours | 5.01 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba Specialty Chemicals | Rep. No. 437A-101 | 1998 | 2018/02/07 | ||||||
藻類 | Navicula pelliculosa | EC50 | 96 | hours | 16 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Contract draft GAI | 1998 | 2018/02/21 | |||||||||
藻類 | Anabaena flos-aquae | EC50 | 96 | hours | 1.2 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Contract draft GAI | 1998 | 2018/02/21 | |||||||||
藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 0.0034 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
藻類 | Selenastrum capricornutum | 生長阻害 | ErC50 | 72 | hours | 0.0027 | mg/L | 11 Japan チャレンジプログラム | 2018/03/11 | ||||||||||
藻類 | Selenastrum capricornutum | 生長阻害 | NOErC | 72 | hours | 0.0018 | mg/L | 11 Japan チャレンジプログラム | 2018/03/18 | ||||||||||
藻類 | Dunaliella tertiolecta | growth inhibition | EC50 | 96 | hours | 3.55 | μg/L | 12 ECHA Information on Registered Substances | 2 | De Lorenzo et al. | 2008 | 2018/02/07 | |||||||
藻類 | Desmodesmus subspicatus | growth inhibition | EC50 | 72 | hours | 1.89 | μg/L | 12 ECHA Information on Registered Substances | 2 | Colgate-Palmolive | Rep. No. 362A-105, without humic acid | 1999 | 2018/02/07 | ||||||
藻類 | Desmodesmus subspicatus | Growth(Area Under Growth Curve) | EC50 | 3 | days | 0.7 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
藻類 | Pseudokirchneriella subcapitata | 72 | hours | 0.2 | μg/L | 4 OECD SIDS (HPVC) | Yang LH, Ying GG, SU HC, Stauber JL, Adams MS and Binet MT | Growth-inhibiting effects of 12 antibacterial agents and their mixtures on the freshwater microalga Pseudokirchneriella subcapitata. | Environmental Toxicology and Chemistry | 2008 | 2018/03/11 | ||||||||
藻類 | Pseudokirchneriella subcapitata | IC50 | 72 | hours | 0.53 | μg/L | 4 OECD SIDS (HPVC) | Yang LH, Ying GG, SU HC, Stauber JL, Adams MS and Binet MT | Growth-inhibiting effects of 12 antibacterial agents and their mixtures on the freshwater microalga Pseudokirchneriella subcapitata. | Environmental Toxicology and Chemistry | 2008 | 2018/03/11 | |||||||
藻類 | Pseudokirchneriella subcapitata | growth inhibition | EC50 | 72 | hours | 4.7 | μg/L | 4 OECD SIDS (HPVC) | Tatarazako N, Ishibashi H, Teshima K, Kishi K, Arizono K | Effects of triclosan on various aquatic organisms. | Environ Sciences | 2004 | 2018/03/11 | ||||||
藻類 | Scenedesmus subspicatus | growth inhibition | ErC10 | 96 | hours | 0.78 | μg/L | 4 OECD SIDS (HPVC) | Wildlife International Ltd | Triclosan: Toxicity mitigation by humic acid during a 96- hour toxicity test with the Freshwater Algae (Scenedesmus subspicatus) | Unpublished report. | 1999 | 2018/03/11 | ||||||
藻類 | Scenedesmus subspicatus | growth inhibition | ErC50 | 96 | hours | 3.5 | μg/L | 4 OECD SIDS (HPVC) | Wildlife International Ltd | Triclosan: Toxicity mitigation by humic acid during a 96- hour toxicity test with the Freshwater Algae (Scenedesmus subspicatus) | Unpublished report. | 1999 | 2018/03/11 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth inhibition | EC50 | 72 | hours | 4.7 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tatarazako et al. | 2004 | 2018/02/07 | |||||||
藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 0.0021 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
藻類 | Pseudokirchneriella subcapitata | EC50 | 96 | hours | 3.4 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Contract draft GAI | 1997 | 2018/02/21 | |||||||||
藻類 | Scenedesmus subspicatus | GROWTH | EC50 | 72 | hours | 120 | ppb | 3 USEPA Pesticide Ecotoxicity Database | R. Petrie | 2008 | 2018/02/21 | ||||||||
藻類 | Scenedesmus subspicatus | growth inhibition | ErC50 | 96 | hours | 1.4 | μg/L | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Acute toxicity of triclosan to Scenedesmus subspicatus. | Analytical Bio-Chemistry Laboratories, Inc. Unpublished Report No. 43118, Ciba-Geigy Corporation. | 1997 | 2018/03/11 | ||||||
藻類 | Selenastrum capricornutum | 生長阻害 | EbC50 | 72 | hours | 0.0021 | mg/L | 11 Japan チャレンジプログラム | 2018/03/11 | ||||||||||
藻類 | Pseudokirchneriella subcapitata | EbC50 | 96 | hours | 4.46 | μg/L | ○ | 4 OECD SIDS (HPVC) | Carolina Ecotox Inc. | Effects of triclosan on the growth and reproduction of aquatic plants. | Unpublished study report No. 21-02-1, Ciba Specialty Chemicals, NC, USA. | 1997 | 2018/03/11 | ||||||
藻類 | Anabaena flos-aquae | ErC10 | 96 | hours | 0.97 | μg/L | ○ | 4 OECD SIDS (HPVC) | Wildlife International Ltd | Triclosan: A 96-hour toxicity test with the freshwater alga (Anabaena flos-aquae). | Unpublished Project Report No. 473A-101, Ciba Specialty Chemicals, NC, USA. | 1998 | 2018/03/11 | ||||||
藻類 | Dunaliella tertiolecta | EC50 | 96 | hours | 3.55 | μg/L | 4 OECD SIDS (HPVC) | Delorenzo ME, Keller JM, Arthur CD, Finnegan MC, Harper HE, Winder VL, Zdankiewicz DL | Toxicity of the antimicrobial compound triclosan and formation of the metabolite methyl-triclosan in estuarine systems. | Environ Toxicol. | 2008 | 2018/03/11 | |||||||
藻類 | Scenedesmus subspicatus | growth inhibition | EbC50 | 72 | hours | 0.7 | μg/L | 4 OECD SIDS (HPVC) | RCC | Toxicity of 14C-FAT 80’023/R) to Scenedesmus subspicatus (OECD – Algae Growth Inhibition Test). | RCC Umweltchemie AG, CH-4452 Itingen, Switzerland. Unpublished Report No. 385637, Ciba-Geigy Limited. | 1995 | 2018/03/11 | ||||||
藻類 | Anabaena flos-aquae | Growth | EC50 | 4 | days | 1.6 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
藻類 | Scenedesmus subspicatus | growth inhibition | ErC50 | 96 | hours | 1.6 | μg/L | 4 OECD SIDS (HPVC) | Wildlife International Ltd | Triclosan: Toxicity mitigation by humic acid during a 96- hour toxicity test with the Freshwater Algae (Scenedesmus subspicatus) | Unpublished report. | 1999 | 2018/03/11 | ||||||
藻類 | Navicula pelliculosa | Growth | EC50 | 4 | days | 19.1 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
藻類 | Selenastrum capricornutum | 生長阻害 | ErC50 | 48 | hours | 0.0025 | mg/L | 11 Japan チャレンジプログラム | 2018/03/14 | ||||||||||
藻類 | Navicula pelliculosa | EbC50 | 96 | hours | 19.1 | μg/L | ○ | 4 OECD SIDS (HPVC) | Carolina Ecotox Inc. | Effects of triclosan on the growth and reproduction of aquatic plants. | Unpublished study report No. 21-02-1, Ciba Specialty Chemicals, NC, USA. | 1997 | 2018/03/11 | ||||||
藻類 | Anabaena flos-aquae | Growth | EC50 | 4 | days | 0.97 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
藻類 | Anabaena flos-aquae | ErC50 | 96 | hours | 1.6 | μg/L | ○ | 4 OECD SIDS (HPVC) | Wildlife International Ltd | Triclosan: A 96-hour toxicity test with the freshwater alga (Anabaena flos-aquae). | Unpublished Project Report No. 473A-101, Ciba Specialty Chemicals, NC, USA. | 1998 | 2018/03/11 | ||||||
藻類 | Desmodesmus subspicatus | Growth(Area Under Growth Curve) | EC50 | 4 | days | 1.4 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||
藻類 | Scenedesmus subspicatus | growth inhibition | ErC50 | 72 | hours | 2.8 | μg/L | 4 OECD SIDS (HPVC) | RCC | Toxicity of 14C-FAT 80’023/R) to Scenedesmus subspicatus (OECD – Algae Growth Inhibition Test). | RCC Umweltchemie AG, CH-4452 Itingen, Switzerland. Unpublished Report No. 385637, Ciba-Geigy Limited. | 1995 | 2018/03/11 | ||||||
藻類 | Pseudokirchneriella subcapitata | Growth | EC50 | 3 | days | 4.7 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | Tatarazako, N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms. | Environ.Sci. | 2004 | 2018/03/06 | |||||
藻類 | Pseudokirchneriella subcapitata | Growth | EC50 | 4 | days | 4.46 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
藻類 | Selenastrum capricornutum | 生長阻害 | NOErC | 48 | hours | 0.001 | mg/L | 11 Japan チャレンジプログラム | 2018/03/18 | ||||||||||
藻類 | Skeletonema costatum | Growth | EC50 | 4 | days | >66 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
藻類 | Anabaena flos-aquae | EbC50 | 96 | hours | 0.97 | μg/L | ○ | 4 OECD SIDS (HPVC) | Carolina Ecotox Inc. | Effects of triclosan on the growth and reproduction of aquatic plants. | Unpublished study report No. 21-02-1, Ciba Specialty Chemicals, NC, USA. | 1997 | 2018/03/11 | ||||||
藻類 | Skeletonema costatum | ErC50 | 96 | hours | >66 | μg/L | ○ | 4 OECD SIDS (HPVC) | Carolina Ecotox Inc. | Effects of triclosan on the growth and reproduction of aquatic plants. | Unpublished study report No. 21-02-1, Ciba Specialty Chemicals, NC, USA. | 1997 | 2018/03/11 | ||||||
藻類 | Desmodesmus subspicatus | Growth rate | EC50 | 3 | days | 2.8 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||
藻類 | Skeletonema costatum | EC50 | 96 | hours | >66 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Contract draft GAI | 1998 | 2018/02/21 | |||||||||
藻類 | Desmodesmus subspicatus | growth rate | NOEC | 72 | hours | 0.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1995 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC10 | 96 | hours | 0.78 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC10 | 96 | hours | 1.46 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | biomass | NOEC | 72 | hours | 0.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1995 | 2016/02/25 | ||||||
藻類 | Navicula pelliculosa | growth rate | EC10 | 96 | hours | 0.1 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | NOEC | 96 | hours | 2.38 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC10 | 96 | hours | 1.4 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | biomass | NOEC | 72 | hours | 0.69 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC10 | 72 | hours | 0.076 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | NOEC | 72 | hours | 0.04 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC10 | 96 | hours | 0.78 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | NOEC | 96 | hours | 0.69 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC10 | 96 | hours | 4.1 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | NOEC | 96 | hours | 0.742 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/02/25 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC10 | 96 | hours | 2 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1997 | 2016/02/25 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth inhibition | EC10 | 72 | hours | 2.7 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tatarazako et al. | 2004 | 2018/02/07 | |||||||
藻類 | Anabaena flos-aquae | growth inhibition | EC10 | 96 | hours | 0.42 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 21-02-1 | 1997 | 2018/02/07 | ||||||
藻類 | Desmodesmus subspicatus | growth inhibition | EC10 | 72 | hours | 0.46 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba Specialty Chemicals | Rep. No. 385837 | 1995 | 2018/02/07 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth inhibition | EC10 | 96 | hours | 1.81 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 21-02-1 | 1997 | 2018/02/07 | ||||||
藻類 | Anabaena flos-aquae | growth inhibition | EC10 | 72 | hours | 1.98 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba Specialty Chemicals | Rep. No. 437A-101 | 1998 | 2018/02/07 | ||||||
藻類 | Navicula pelliculosa | NOEL | 96 | hours | <0.5 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Contract draft GAI | 1998 | 2018/02/21 | |||||||||
藻類 | Anabaena flos-aquae | NOEL | 96 | hours | <0.5 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Contract Draft GAI | 1998 | 2018/02/21 | |||||||||
藻類 | Pseudokirchneriella subcapitata | NOEL | 96 | hours | 2.5 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Contract draft GAI | 1997 | 2018/02/21 | |||||||||
藻類 | Scenedesmus subspicatus | GROWTH | NOEL | 72 | hours | 40 | ppb | 3 USEPA Pesticide Ecotoxicity Database | R. Petrie | 2008 | 2018/02/21 | ||||||||
藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 0.001 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
藻類 | Dunaliella tertiolecta | growth inhibition | NOEC | 96 | hours | 1.6 | μg/L | 12 ECHA Information on Registered Substances | 2 | De Lorenzo et al. | 2008 | 2018/02/07 | |||||||
藻類 | Skeletonema costatum | growth inhibition | EC10 | 96 | hours | >66 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 21-02-1 | 1997 | 2018/02/07 | ||||||
藻類 | Desmodesmus subspicatus | growth inhibition | EC10 | 72 | hours | 1.03 | μg/L | 12 ECHA Information on Registered Substances | 2 | Colgate-Palmolive | Rep. No. 362A-105, without humic acid | 1999 | 2018/02/07 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth inhibition | NOEC | 72 | hours | 0.53 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tamura et al. | 2012 | 2018/02/07 | |||||||
藻類 | Desmodesmus subspicatus | growth inhibition | EC10 | 72 | hours | 0.076 | μg/L | 12 ECHA Information on Registered Substances | 1 | Ciba Specialty Chem. | Rep. No.A34918 | 2006 | 2018/02/07 | ||||||
藻類 | Navicula pelliculosa | growth inhibition | EC10 | 96 | hours | 12.66 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 21-02-1 | 1997 | 2018/02/07 | ||||||
藻類 | Desmodesmus subspicatus | growth inhibition | EC10 | 72 | hours | 1.03 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 43118 | 1997 | 2018/02/07 | ||||||
藻類 | Scenedesmus subspicatus | growth inhibition | EC10 | 96 | hours | 2.4 | μg/L | 4 OECD SIDS (HPVC) | Wildlife International Ltd | Triclosan: Toxicity mitigation by humic acid during a 96- hour toxicity test with the Freshwater Algae (Scenedesmus subspicatus) | Unpublished report. | 1999 | 2018/03/11 | ||||||
藻類 | Desmodesmus subspicatus | Growth(Area Under Growth Curve) | NOEC | 4 | days | 0.69 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||
藻類 | Scenedesmus subspicatus | growth inhibition | LOEC | 72 | hours | 1.2 | μg/L | 4 OECD SIDS (HPVC) | RCC | Toxicity of 14C-FAT 80’023/R) to Scenedesmus subspicatus (OECD – Algae Growth Inhibition Test). | RCC Umweltchemie AG, CH-4452 Itingen, Switzerland. Unpublished Report No. 385637, Ciba-Geigy Limited. | 1995 | 2018/03/11 | ||||||
藻類 | Scenedesmus subspicatus | growth inhibition | NOEC | 96 | hours | 2.38 | μg/L | 4 OECD SIDS (HPVC) | Wildlife International Ltd | Triclosan: Toxicity mitigation by humic acid during a 96- hour toxicity test with the Freshwater Algae (Scenedesmus subspicatus) | Unpublished report. | 1999 | 2018/03/11 | ||||||
藻類 | Scenedesmus subspicatus | growth inhibition | NOEC | 96 | hours | 0.742 | μg/L | 4 OECD SIDS (HPVC) | Wildlife International Ltd | Triclosan: Toxicity mitigation by humic acid during a 96- hour toxicity test with the Freshwater Algae (Scenedesmus subspicatus) | Unpublished report. | 1999 | 2018/03/11 | ||||||
藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 0.001 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
藻類 | Desmodesmus subspicatus | Growth(Area Under Growth Curve/速度法) | NOEC | 3 | days | 0.5 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
藻類 | Scenedesmus subspicatus | growth inhibition | LOEC | 72 | hours | 1.2 | μg/L | 4 OECD SIDS (HPVC) | RCC | Toxicity of 14C-FAT 80’023/R) to Scenedesmus subspicatus (OECD – Algae Growth Inhibition Test). | RCC Umweltchemie AG, CH-4452 Itingen, Switzerland. Unpublished Report No. 385637, Ciba-Geigy Limited. | 1995 | 2018/03/11 | ||||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | NOEC | 3 | days | 1 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | (独)国立環境研究所 | 平成18年度化学物質環境リスク評価検討調査(第7 次とりまとめ等に係る調査)報告書 | 2007 | 2018/03/17 | ||||||
藻類 | Scenedesmus subspicatus | growth inhibition | NOEC | 72 | hours | 0.5 | μg/L | 4 OECD SIDS (HPVC) | RCC | Toxicity of 14C-FAT 80’023/R) to Scenedesmus subspicatus (OECD – Algae Growth Inhibition Test). | RCC Umweltchemie AG, CH-4452 Itingen, Switzerland. Unpublished Report No. 385637, Ciba-Geigy Limited. | 1995 | 2018/03/11 | ||||||
藻類 | Pseudokirchneriella subcapitata | Growth(Area Under Growth Curve) | NOEC | 3 | days | 1 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | 環境庁 | 平成8年度 生態影響試験 | 1997 | 2018/03/17 | ||||||
藻類 | Scenedesmus subspicatus | growth inhibition | NOEC | 96 | hours | 0.69 | μg/L | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Acute toxicity of triclosan to Scenedesmus subspicatus. | Analytical Bio-Chemistry Laboratories, Inc. Unpublished Report No. 43118, Ciba-Geigy Corporation. | 1997 | 2018/03/11 | ||||||
藻類 | Pseudokirchneriella subcapitata | Growth(Area Under Growth Curve) | EC50 | 3 | days | 2.1 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | 環境庁 | 平成8年度 生態影響試験 | 1997 | 2018/03/17 | ||||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | EC50 | 3 | days | 3.4 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | (独)国立環境研究所 | 平成18年度化学物質環境リスク評価検討調査(第7 次とりまとめ等に係る調査)報告書 | 2007 | 2018/03/17 | ||||||
藻類 | Scenedesmus subspicatus | growth inhibition | NOEC | 72 | hours | 0.5 | μg/L | 4 OECD SIDS (HPVC) | RCC | Toxicity of 14C-FAT 80’023/R) to Scenedesmus subspicatus (OECD – Algae Growth Inhibition Test). | RCC Umweltchemie AG, CH-4452 Itingen, Switzerland. Unpublished Report No. 385637, Ciba-Geigy Limited. | 1995 | 2018/03/11 | ||||||
藻類 | Anabaena flos-aquae | NOEC | 96 | hours | 0.81 | μg/L | ○ | 4 OECD SIDS (HPVC) | Wildlife International Ltd | Triclosan: A 96-hour toxicity test with the freshwater alga (Anabaena flos-aquae). | Unpublished Project Report No. 473A-101, Ciba Specialty Chemicals, NC, USA. | 1998 | 2018/03/11 | ||||||
藻類 | Selenastrum capricornutum | 生長阻害 | NOEC | 72 | hours | 0.001 | mg/L | 11 Japan チャレンジプログラム | 2018/03/14 | ||||||||||
藻類 | Skeletonema costatum | NOEL | 96 | hours | 12.6 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Contract draft GAI | 1998 | 2018/02/21 | |||||||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | >240 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | >150 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 2 | days | 390 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | >130 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 2 | days | 420 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | >120 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | >130 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 2 | days | >180 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Mortality | EC50 | 2 | days | 390 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 2 | days | 420 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | ||||||
甲殻類 | Daphnia magna | Cellular Effects | 3 | days | 40 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hannas,B.R., Y.H. Wang, S. Thomson, G. Kwon, H. Li, and G.A. LeBlanc | Regulation and Dysregulation of Vitellogenin mRNA Accumulation in Daphnids (Daphnia magna) | Aquat. Toxicol.101(2): 351-357 | 2011 | 2016/03/25 | |||||||
甲殻類 | Ceriodaphnia dubia | Reproduction | IC25 | 6 | days | 170 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Reproduction | LOEC | 13 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Reproduction | LOEC | 13 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Mortality | NOEC | 13 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Mysidopsis bahia | Mortality | LC50 | 2 | days | 95.6 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Perron,M.M., K.T. Ho, M.G. Cantwell, R.M. Burgess, and M.C. Pelletier | Effects of Triclosan on Marine Benthic and Epibenthic Organisms | Environ. Toxicol. Chem.31(8): 1861-1866 | 2012 | 2018/03/19 | |||||
甲殻類 | Mysidopsis bahia | Mortality | LC50 | 1 | days | 202 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Perron,M.M., K.T. Ho, M.G. Cantwell, R.M. Burgess, and M.C. Pelletier | Effects of Triclosan on Marine Benthic and Epibenthic Organisms | Environ. Toxicol. Chem.31(8): 1861-1866 | 2012 | 2018/03/19 | |||||
甲殻類 | Mysidopsis bahia | Mortality | LC50 | 4 | days | 74.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Perron,M.M., K.T. Ho, M.G. Cantwell, R.M. Burgess, and M.C. Pelletier | Effects of Triclosan on Marine Benthic and Epibenthic Organisms | Environ. Toxicol. Chem.31(8): 1861-1866 | 2012 | 2018/03/19 | |||||
甲殻類 | Mysidopsis bahia | Mortality | LC50 | 3 | days | 78.4 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Perron,M.M., K.T. Ho, M.G. Cantwell, R.M. Burgess, and M.C. Pelletier | Effects of Triclosan on Marine Benthic and Epibenthic Organisms | Environ. Toxicol. Chem.31(8): 1861-1866 | 2012 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Mortality | LOEC | 13 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 0.835 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., E.J. Litoff, and W.S. Baldwin | The HR96 Activator, Atrazine, Reduces Sensitivity of D. magna to Triclosan and DHA | Chemosphere128:299-306 | 2015 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | LOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Palaemonetes sp. Palaemonetes pugio. | LC50 | 24 | hours | 482 | μg/L | 4 OECD SIDS (HPVC) | Delorenzo ME, Keller JM, Arthur CD, Finnegan MC, Harper HE, Winder VL, Zdankiewicz DL | Toxicity of the antimicrobial compound triclosan and formation of the metabolite methyl-triclosan in estuarine systems. | Environ Toxicol. | 2008 | 2018/03/11 | |||||||
甲殻類 | Palaemonetes sp. Palaemonetes pugio. | LC50 | 24 | hours | 620 | μg/L | 4 OECD SIDS (HPVC) | Delorenzo ME, Keller JM, Arthur CD, Finnegan MC, Harper HE, Winder VL, Zdankiewicz DL | Toxicity of the antimicrobial compound triclosan and formation of the metabolite methyl-triclosan in estuarine systems. | Environ Toxicol. | 2008 | 2018/03/11 | |||||||
甲殻類 | Palaemonetes sp. Palaemonetes pugio. | LC50 | 96 | hours | 154 | μg/L | 4 OECD SIDS (HPVC) | Delorenzo ME, Keller JM, Arthur CD, Finnegan MC, Harper HE, Winder VL, Zdankiewicz DL | Toxicity of the antimicrobial compound triclosan and formation of the metabolite methyl-triclosan in estuarine systems. | Environ Toxicol. | 2008 | 2018/03/11 | |||||||
甲殻類 | Palaemonetes sp. Palaemonetes pugio. | LC50 | 96 | hours | 651 | μg/L | 4 OECD SIDS (HPVC) | Delorenzo ME, Keller JM, Arthur CD, Finnegan MC, Harper HE, Winder VL, Zdankiewicz DL | Toxicity of the antimicrobial compound triclosan and formation of the metabolite methyl-triclosan in estuarine systems. | Environ Toxicol. | 2008 | 2018/03/11 | |||||||
甲殻類 | Palaemonetes sp. Palaemonetes pugio. | LC50 | 96 | hours | 305 | μg/L | 4 OECD SIDS (HPVC) | Delorenzo ME, Keller JM, Arthur CD, Finnegan MC, Harper HE, Winder VL, Zdankiewicz DL | Toxicity of the antimicrobial compound triclosan and formation of the metabolite methyl-triclosan in estuarine systems. | Environ Toxicol. | 2008 | 2018/03/11 | |||||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Enzyme | NOEC | 0.67 | days | 0.75 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., E.J. Litoff, and W.S. Baldwin | The HR96 Activator, Atrazine, Reduces Sensitivity of D. magna to Triclosan and DHA | Chemosphere128:299-306 | 2015 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 0.67 | days | 0.75 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., E.J. Litoff, and W.S. Baldwin | The HR96 Activator, Atrazine, Reduces Sensitivity of D. magna to Triclosan and DHA | Chemosphere128:299-306 | 2015 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 0.67 | days | 0.75 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., E.J. Litoff, and W.S. Baldwin | The HR96 Activator, Atrazine, Reduces Sensitivity of D. magna to Triclosan and DHA | Chemosphere128:299-306 | 2015 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 0.345 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Daphnia magna | Biochemical | NOEC | 4 | days | 0.25 | μM | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sengupta,N., P.D. Gerard, and W.S. Baldwin | Perturbations in Polar Lipids, Starvation Survival and Reproduction Following Exposure to Unsaturated Fatty Acids or Environmental Toxicants in Daphnia magna | Chemosphere144:2302-2311 | 2016 | 2018/03/19 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | NOEC | 7 | days | 50 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Mortality | 2 | days | 1000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | ||||||
甲殻類 | Daphnia magna | Growth | NOEL | 30 | days | 10 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Flaherty,C.M., and S.I. Dodson | Effects of Pharmaceuticals on Daphnia Survival, Growth, and Reproduction | Chemosphere61(2): 200-207 | 2005 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Intoxication | NOEL | 2 | days | 180 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Intoxication | NOEL | 2 | days | 240 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | ||||||
甲殻類 | Daphnia magna | Mortality | NOEL | 30 | days | 10 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Flaherty,C.M., and S.I. Dodson | Effects of Pharmaceuticals on Daphnia Survival, Growth, and Reproduction | Chemosphere61(2): 200-207 | 2005 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Intoxication | NOEL | 2 | days | 100 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Intoxication | NOEL | 2 | days | 240 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | ||||||
甲殻類 | Ceriodaphnia dubia | Reproduction | NOEC | 7 | days | 6 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 18 | μg/L | Unionized | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | NOEC | 7 | days | 339 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Mortality | NOEC | 21 | days | 200 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Population | LOEL | 30 | days | 10 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Flaherty,C.M., and S.I. Dodson | Effects of Pharmaceuticals on Daphnia Survival, Growth, and Reproduction | Chemosphere61(2): 200-207 | 2005 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 88 | μg/L | Unionized | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 200 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 6 | days | 220 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Reproduction | IC50 | 7 | days | 85.48 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cho,E.A. | Bioturbation as a Novel Method to Characterize the Toxicity of Aquatic Sediment | Ph.D. Thesis, North Carolina State University, Raleigh, NC:153 p. | 2005 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | >115 | μg/L | Unionized | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | >180 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | >410 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/02 | |||||
甲殻類 | Daphnia magna | Reproduction | NOEL | 30 | days | 10 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Flaherty,C.M., and S.I. Dodson | Effects of Pharmaceuticals on Daphnia Survival, Growth, and Reproduction | Chemosphere61(2): 200-207 | 2005 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Reproduction | NOEC | 7 | days | 182 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 40 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Reproduction | EC50 | 7 | days | 220 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | Tatarazako, N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms. | Environ.Sci. | 2004 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.191 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1990 | 2016/02/24 | ||||||
甲殻類 | Daphnia magna | mobility | EC100 | 48 | hours | >0.18 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2016/02/24 | ||||||
甲殻類 | Daphnia magna | mobility | EC0 | 48 | hours | 0.0697 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1990 | 2016/02/24 | ||||||
甲殻類 | Ceriodaphnia sp. | mortality | LC50 | 48 | hours | 0.18 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1991 | 2016/02/25 | ||||||
甲殻類 | Ceriodaphnia sp. | mortality | LC50 | 48 | hours | 0.13 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1991 | 2016/02/25 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | >0.18 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2016/02/24 | ||||||
甲殻類 | Daphnia magna | mobility | EC0 | 48 | hours | >=0.18 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2006 | 2016/02/24 | ||||||
甲殻類 | Daphnia magna | mobility | EC100 | 48 | hours | 1.2 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1990 | 2016/02/24 | ||||||
甲殻類 | Ceriodaphnia sp. | mortality | LC50 | 48 | hours | 0.24 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1991 | 2016/02/25 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.39 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1990 | 2016/02/25 | ||||||
甲殻類 | Ceriodaphnia sp. | mortality | LC50 | 48 | hours | 0.41 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1991 | 2016/02/25 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 330 | μg/L | 12 ECHA Information on Registered Substances | 2 | Peng et al. | 2013 | 2018/02/07 | |||||||
甲殻類 | Ceriodaphnia sp. | mortality | LC50 | 48 | hours | 410 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 1011-0691-6278-132 | 1991 | 2018/02/07 | ||||||
甲殻類 | Ceriodaphnia sp. | mortality | LC50 | 48 | hours | 180 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 1011-0691-6278-132 | 1991 | 2018/02/07 | ||||||
甲殻類 | Ceriodaphnia sp. | mortality | LC50 | 48 | hours | 240 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 1011-0691-6278-132 | 1991 | 2018/02/07 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | >180 | μg/L | above the solubility limit | 12 ECHA Information on Registered Substances | 1 | Ciba Specialty Chem. | Rep. No.A34931 | 2006 | 2018/02/07 | |||||
甲殻類 | Palaemonetes sp. Palaemonetes pugio | LC50 | 96 | hours | 154 | μg/L | 12 ECHA Information on Registered Substances | 2 | De Lorenzo et al. | 2008 | 2018/03/03 | ||||||||
甲殻類 | Daphnia magna | mortality | EC50 | 48 | hours | 390 | μg/L | 12 ECHA Information on Registered Substances | 2 | Orvos et al. | 2002 | 2018/02/07 | |||||||
甲殻類 | Ceriodaphnia sp. | mortality | LC50 | 48 | hours | 130 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Corp. | Rep. No. 1011-0691-6278-132 | 1991 | 2018/03/03 | ||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 420 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C. Laird | 1990 | 2018/02/21 | |||||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 420 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C. Laird | 1990 | 2018/02/21 | |||||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 24 | hours | 0.39 | mg/L | 11 Japan チャレンジプログラム | 2018/03/12 | ||||||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 48 | hours | 0.27 | mg/L | 11 Japan チャレンジプログラム | 2018/03/12 | ||||||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 390 | μg/L | 12 ECHA Information on Registered Substances | 2 | Procter & Gamble | Rep. No. 38656 | 1990 | 2018/02/07 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC100 | 48 | hours | 0.56 | mg/L | 11 Japan チャレンジプログラム | 2018/03/12 | ||||||||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 130 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 180 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tamura et al. | 2013 | 2018/02/07 | |||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 338 | μg/L | 12 ECHA Information on Registered Substances | 2 | Wang et al. | 2013 | 2018/02/07 | |||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 260 | μg/L | 12 ECHA Information on Registered Substances | 2 | Harada et al. | 2008 | 2018/02/07 | |||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 191 | μg/L | 12 ECHA Information on Registered Substances | 1 | Ciba-Geigy AG | Proj. No. 262923 | 1990 | 2018/02/07 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | NOEC | 48 | hours | 0.1 | mg/L | 11 Japan チャレンジプログラム | 2018/03/14 | ||||||||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 180 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 303 | μg/L | 4 OECD SIDS (HPVC) | Ferrari B, Paxeus N, Pollio A, Andreozzi R, Marotta R, Vogna D, Lyberatos G, Garric J | Fate and effect of triclosan in the aquatic ecosystems: data for a risk assessment [poster]. | In: Society of Environmental Toxicology and Chemistry Annual Meeting in Europe; 2002 May 12 – 16; Vienna, Austria. Brussels (BE): SETAC Europe. | 2002 | 2018/03/11 | |||||||
甲殻類 | Ceriodaphnia dubia | EC50 | 48 | hours | 123 | μg/L | 4 OECD SIDS (HPVC) | Ferrari B, Paxeus N, Pollio A, Andreozzi R, Marotta R, Vogna D, Lyberatos G, Garric J | Fate and effect of triclosan in the aquatic ecosystems: data for a risk assessment [poster]. | In: Society of Environmental Toxicology and Chemistry Annual Meeting in Europe; 2002 May 12 – 16; Vienna, Austria. Brussels (BE): SETAC Europe. | 2002 | 2018/03/11 | |||||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 120 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | EC50 | 48 | hours | 240 | 4 OECD SIDS (HPVC) | Orvos DR, Versteeg DJ, Inauen J, Capdevielle M, Rothenstein A. and Cunningham V | Aquatic Toxicity of Triclosan. Environmental Toxicology and Chemistry | 2002 | 2018/03/11 | |||||||||
甲殻類 | Ceriodaphnia dubia | EC50 | 48 | hours | 420 | 4 OECD SIDS (HPVC) | Orvos DR, Versteeg DJ, Inauen J, Capdevielle M, Rothenstein A. and Cunningham V | Aquatic Toxicity of Triclosan. Environmental Toxicology and Chemistry | 2002 | 2018/03/11 | |||||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 0.27 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | >180 | ppb | 3 USEPA Pesticide Ecotoxicity Database | R. Petrie | 2008 | 2018/02/21 | |||||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 390 | ppb | 3 USEPA Pesticide Ecotoxicity Database | J. Edwards | 1994 | 2018/02/21 | |||||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 550 | μg/L | ○ | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Acute toxicity of D1063.01 to Daphnia magna. | Analytical Bio-Chemistry Laboratories, Inc. Unpublished report, Proctor & Gamble Company. | 1990 | 2018/03/11 | ||||||
甲殻類 | Ceriodaphnia dubia | EC50 | 48 | hours | 130 | 4 OECD SIDS (HPVC) | Orvos DR, Versteeg DJ, Inauen J, Capdevielle M, Rothenstein A. and Cunningham V | Aquatic Toxicity of Triclosan. Environmental Toxicology and Chemistry | 2002 | 2018/03/11 | |||||||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 2 | days | 390 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 410 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 115 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 150 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | NOEC | 48 | hours | 100 | μg/L | ○ | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Acute toxicity of D1063.01 to Daphnia magna. | Analytical Bio-Chemistry Laboratories, Inc. Unpublished report, Proctor & Gamble Company. | 1990 | 2018/03/11 | ||||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 240 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | EC50 | 48 | hours | 180 | 4 OECD SIDS (HPVC) | Orvos DR, Versteeg DJ, Inauen J, Capdevielle M, Rothenstein A. and Cunningham V | Aquatic Toxicity of Triclosan. Environmental Toxicology and Chemistry | 2002 | 2018/03/11 | |||||||||
甲殻類 | Ceriodaphnia dubia | Mortality | EC50 | 2 | days | 130 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 2 | days | 270 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | 環境庁 | 平成8年度 生態影響試験 | 1997 | 2018/03/06 | ||||||
甲殻類 | Daphnia magna | EC50 | 24 | hours | 390 | μg/L | ○ | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Acute toxicity of D1063.01 to Daphnia magna. | Analytical Bio-Chemistry Laboratories, Inc. Unpublished report, Proctor & Gamble Company. | 1990 | 2018/03/11 | ||||||
甲殻類 | Daphnia magna | mobility | NOEL | 48 | hours | 0.1 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1990 | 2016/02/25 | ||||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 0.026 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1990 | 2016/02/24 | ||||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 0.182 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2016/03/02 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | NOEC | 7 | days | 0.05 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2016/03/02 | ||||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 0.006 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2016/03/02 | ||||||
甲殻類 | Ceriodaphnia dubia | mortality | NOEC | 7 | days | 0.039 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1993 | 2016/03/02 | ||||||
甲殻類 | Daphnia magna | reproduction | LOEC | 21 | days | 0.13 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1990 | 2016/02/24 | ||||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 8 | days | 30 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tamura et al. | 2012 | 2018/02/07 | |||||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 6 | μg/L | 12 ECHA Information on Registered Substances | 2 | Procter & Gamble | Rep. No. 92-01-2080 | 1993 | 2018/02/07 | ||||||
甲殻類 | Daphnia magna | reproduction | EC10 | 21 | days | 9 | μg/L | 12 ECHA Information on Registered Substances | 2 | Peng et al. | 2013 | 2018/02/07 | |||||||
甲殻類 | Daphnia magna | NOEL | 48 | hours | 100 | ppb | 3 USEPA Pesticide Ecotoxicity Database | J. Edwards | 1994 | 2018/02/21 | |||||||||
甲殻類 | Daphnia magna | EGGHATCH, SURVIVE | EC50 | 21 | days | 139 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B.Montague | 1995 | 2018/02/21 | ||||||||
甲殻類 | Daphnia magna | NOEL | 48 | hours | 180 | ppb | 3 USEPA Pesticide Ecotoxicity Database | R. Petrie | 2008 | 2018/02/21 | |||||||||
甲殻類 | Daphnia magna | NOEL | 48 | hours | 240 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C. Laird | 1990 | 2018/02/21 | |||||||||
甲殻類 | Daphnia magna | NOEC | 21 | days | 0.00034 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
甲殻類 | Chironomus yoshimatsui | LOEC | 28 | days | 186 | mg/kg | 11 Japan チャレンジプログラム | 2018/03/18 | |||||||||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 182 | μg/L | 12 ECHA Information on Registered Substances | 2 | Procter & Gamble | Rep. No. 92-01-2080 | 1993 | 2018/02/07 | ||||||
甲殻類 | Daphnia magna | 繁殖阻害 | ErC50 | 21 | days | 5.5 | μg/L | 11 Japan チャレンジプログラム | 2018/03/12 | ||||||||||
甲殻類 | Daphnia magna | LC50 | 21 | days | 140 | μg/L | 11 Japan チャレンジプログラム | 2018/03/12 | |||||||||||
甲殻類 | Ceriodaphnia dubia | reproduction | EC10 | 7 | days | 132 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tatarazako et al. | 2004 | 2018/02/07 | |||||||
甲殻類 | Chironomus yoshimatsui | 羽化率 | EC50 | 28 | days | 180 | mg/kg | 11 Japan チャレンジプログラム | 2018/03/18 | ||||||||||
甲殻類 | Ceriodaphnia dubia | reprod. | NOEC | 7 | days | 6 | μg/L | 4 OECD SIDS (HPVC) | Springborn Laboratories | Chronic toxicity evaluation of D1063.02R using Ceriodaphnia dubia under Static-renewal Conditions. | Jop, K. M (ed). Unpublished Report No. 92-01-4080, Proctor & Gamble Company. | 1993 | 2018/03/11 | ||||||
甲殻類 | Ceriodaphnia dubia | surviv. | NOEC | 7 | days | 50 | μg/L | 4 OECD SIDS (HPVC) | Springborn Laboratories | Chronic toxicity evaluation of D1063.02R using Ceriodaphnia dubia under Static-renewal Conditions. | Jop, K. M (ed). Unpublished Report No. 92-01-4080, Proctor & Gamble Company. | 1993 | 2018/03/11 | ||||||
甲殻類 | Ceriodaphnia dubia | surviv. | LOEC | 7 | days | 108 | μg/L | 4 OECD SIDS (HPVC) | Springborn Laboratories | Chronic toxicity evaluation of D1063.02R using Ceriodaphnia dubia under Static-renewal Conditions. | Jop, K. M (ed). Unpublished Report No. 92-01-4080, Proctor & Gamble Company. | 1993 | 2018/03/11 | ||||||
甲殻類 | Daphnia magna | reprod. | LOEC | 21 | days | 132 | μg/L | ○ | 4 OECD SIDS (HPVC) | RCC | Influence of FAT 80’023/Q on the reproduction of Daphnia magna. | RCC Umweltchemie AG, CH-4452 Itingen, Switzerland. Unpublished report, Ciba-Geigy Corporation. | 1990 | 2018/03/11 | |||||
甲殻類 | Ceriodaphnia dubia | 7 | days | 8.5 | μg/L | 4 OECD SIDS (HPVC) | Springborn Laboratories | Chronic toxicity evaluation of D1063.02R using Ceriodaphnia dubia under Static-renewal Conditions. | Jop, K. M (ed). Unpublished Report No. 92-01-4080, Proctor & Gamble Company. | 1993 | 2018/03/11 | ||||||||
甲殻類 | Ceriodaphnia dubia | reprod. | LOEC | 7 | days | 339 | μg/L | 4 OECD SIDS (HPVC) | Springborn Laboratories | Chronic toxicity evaluation of D1063.02R using Ceriodaphnia dubia under Static-renewal Conditions. | Jop, K. M (ed). Unpublished Report No. 92-01-4080, Proctor & Gamble Company. | 1993 | 2018/03/11 | ||||||
甲殻類 | Ceriodaphnia dubia | NOEC | 7 | days | 4 | μg/L | 4 OECD SIDS (HPVC) | Ferrari B, Paxeus N, Pollio A, Andreozzi R, Marotta R, Vogna D, Lyberatos G, Garric J | Fate and effect of triclosan in the aquatic ecosystems: data for a risk assessment [poster]. | In: Society of Environmental Toxicology and Chemistry Annual Meeting in Europe; 2002 May 12 – 16; Vienna, Austria. Brussels (BE): SETAC Europe. | 2002 | 2018/03/11 | |||||||
甲殻類 | Daphnia magna | surviv. | NOEC | 21 | days | 132 | μg/L | ○ | 4 OECD SIDS (HPVC) | RCC | Influence of FAT 80’023/Q on the reproduction of Daphnia magna. | RCC Umweltchemie AG, CH-4452 Itingen, Switzerland. Unpublished report, Ciba-Geigy Corporation. | 1990 | 2018/03/11 | |||||
甲殻類 | Ceriodaphnia dubia | IC50 | 7 | days | 220 | μg/L | 4 OECD SIDS (HPVC) | Tatarazako N, Ishibashi H, Teshima K, Kishi K, Arizono K | Effects of triclosan on various aquatic organisms. | Environ Sciences | 2004 | 2018/03/11 | |||||||
甲殻類 | Daphnia magna | EGGHATCH, SURVIVE | NOEL | 21 | days | <40 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B.Montague | 1995 | 2018/02/21 | ||||||||
甲殻類 | Daphnia magna | EC50 | 21 | days | 0.0055 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
甲殻類 | Daphnia magna | NOEL | 48 | hours | 240 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C. Laird | 1990 | 2018/02/21 | |||||||||
甲殻類 | Ceriodaphnia dubia | surviv. | NOEC | 7 | days | 339 | μg/L | 4 OECD SIDS (HPVC) | Springborn Laboratories | Chronic toxicity evaluation of D1063.02R using Ceriodaphnia dubia under Static-renewal Conditions. | Jop, K. M (ed). Unpublished Report No. 92-01-4080, Proctor & Gamble Company. | 1993 | 2018/03/11 | ||||||
甲殻類 | Ceriodaphnia dubia | 7 | days | 248 | μg/L | 4 OECD SIDS (HPVC) | Springborn Laboratories | Chronic toxicity evaluation of D1063.02R using Ceriodaphnia dubia under Static-renewal Conditions. | Jop, K. M (ed). Unpublished Report No. 92-01-4080, Proctor & Gamble Company. | 1993 | 2018/03/11 | ||||||||
甲殻類 | Ceriodaphnia dubia | Reproduction | NOEC | 7 | days | 6 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 30 | days | >100 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Flaherty, C.M., and S.I. Dodson | Effects of Pharmaceuticals on Daphnia Survival, Growth, and Reproduction. | Chemosphere | 2005 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Reproduction | NOEC | 7 | days | 51.8 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Chironomus yoshimatsui | NOEC | 28 | days | 124 | mg/kg | 11 Japan チャレンジプログラム | 2018/03/18 | |||||||||||
甲殻類 | Ceriodaphnia dubia | Reproduction | NOEC | 7 | days | 182 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 40 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | reprod. | LOEC | 7 | days | 12 | μg/L | 4 OECD SIDS (HPVC) | Springborn Laboratories | Chronic toxicity evaluation of D1063.02R using Ceriodaphnia dubia under Static-renewal Conditions. | Jop, K. M (ed). Unpublished Report No. 92-01-4080, Proctor & Gamble Company. | 1993 | 2018/03/11 | ||||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 18 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Daphnia magna | Sex Ratio | NOEC | 30 | days | 1 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Flaherty, C.M., and S.I. Dodson | Effects of Pharmaceuticals on Daphnia Survival, Growth, and Reproduction. | Chemosphere | 2005 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | Reproduction | NOEC | 7 | days | 5.6 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/06 | |||||
甲殻類 | Ceriodaphnia dubia | reprod. | NOEC | 7 | days | 182 | μg/L | 4 OECD SIDS (HPVC) | Springborn Laboratories | Chronic toxicity evaluation of D1063.02R using Ceriodaphnia dubia under Static-renewal Conditions. | Jop, K. M (ed). Unpublished Report No. 92-01-4080, Proctor & Gamble Company. | 1993 | 2018/03/11 | ||||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 0.34 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | 環境庁 | 平成8年度 生態影響試験 | 1997 | 2018/03/06 | ||||||
甲殻類 | Daphnia magna | 繁殖阻害 | LOErC | 21 | days | 0.6 | μg/L | 11 Japan チャレンジプログラム | 2018/03/12 | ||||||||||
甲殻類 | Daphnia magna | 繁殖阻害 | NOErC | 21 | days | 0.34 | μg/L | 11 Japan チャレンジプログラム | 2018/03/12 | ||||||||||
甲殻類 | Daphnia magna | reprod. | NOEC | 21 | days | 40 | μg/L | ○ | 4 OECD SIDS (HPVC) | RCC | Influence of FAT 80’023/Q on the reproduction of Daphnia magna. | RCC Umweltchemie AG, CH-4452 Itingen, Switzerland. Unpublished report, Ciba-Geigy Corporation. | 1990 | 2018/03/11 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEC | 61 | days | 34.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Development | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEL | 4 | days | 100 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Histological | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LOEC | 61 | days | 71.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Behavior | LOEL | 95 | days | 71.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | NOEC | 35 | days | 71.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Development | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Biochemical | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Development | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Morphology | LOEL | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Growth | LOEL | 7 | days | 1000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LOEL | 35 | days | 71.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEC | 35 | days | 15.1 | μg/L | Unionized | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Morphology | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LOEC | 14 | days | 313 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Behavior | LOEC | 8 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Morphology | LOEL | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LOEL | 14 | days | 313 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Morphology | LOEC | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LOEC | 35 | days | 71.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Danio rerio (Zebrafish) | No Group Code | 5 | days | 80 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Padilla,S., D. Corum, B. Padnos, D.L. Hunter, A. Beam, K.A. Houck, N. Sipes, N. Kleinstreuer, T. Knudsen, D.J. Dix, and | Zebrafish Developmental Screening of the ToxCast Phase I Chemical Library | Reprod. Toxicol.33(2): 174-187 | 2012 | 2016/03/25 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 3 | days | 1800 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, I.J. Kang, J. Moroishi, Y. Shimasaki, and Y. Oshima | Pharmaceuticals and Personal Care Products Toxicity to Japanese Medaka Fish (Oryzias latipes) | J. Fac. Agric. Kyushu Univ.54(2): 407-411 | 2009 | 2018/03/19 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 1 | days | 2300 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, I.J. Kang, J. Moroishi, Y. Shimasaki, and Y. Oshima | Pharmaceuticals and Personal Care Products Toxicity to Japanese Medaka Fish (Oryzias latipes) | J. Fac. Agric. Kyushu Univ.54(2): 407-411 | 2009 | 2018/03/19 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Physiological | LOEC | 6 | days | 5 | ng/egg ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S.G. Kim, M. Seki, I.J. Kang, T. Hano, Y. Shimasaki, and Y. Oshima | In Ovo Nanoinjection of Triclosan, Diclofenac and Carbamazepine Affects Embryonic Development of Medaka Fish (Oryzias latipes) | Chemosphere79:966-973 | 2010 | 2018/03/19 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | 4 | days | 1000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, I.J. Kang, J. Moroishi, Y. Shimasaki, and Y. Oshima | Pharmaceuticals and Personal Care Products Toxicity to Japanese Medaka Fish (Oryzias latipes) | J. Fac. Agric. Kyushu Univ.54(2): 407-411 | 2009 | 2018/03/19 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Genetic | LOEC | 1 | days | 1700 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., Y. Kato-Unoki, T. Furuta, K. Nakayama, H. Satone, Y. Shimasaki, T. Honjo, and Y. Oshima | Molecular Cloning, Sequencing, and Gene Expression Analysis of Tributyltin-Binding Protein Type 1 in Japanese Medaka Fish, Oryzias latipes | Zool. Sci.28(4): 281-285 | 2011 | 2018/03/19 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | 2 | days | 3000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, I.J. Kang, J. Moroishi, Y. Shimasaki, and Y. Oshima | Pharmaceuticals and Personal Care Products Toxicity to Japanese Medaka Fish (Oryzias latipes) | J. Fac. Agric. Kyushu Univ.54(2): 407-411 | 2009 | 2018/03/19 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | 4 | days | 9 | ng/egg ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S.G. Kim, M. Seki, I.J. Kang, T. Hano, Y. Shimasaki, and Y. Oshima | In Ovo Nanoinjection of Triclosan, Diclofenac and Carbamazepine Affects Embryonic Development of Medaka Fish (Oryzias latipes) | Chemosphere79:966-973 | 2010 | 2018/03/19 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | NOEC | 4 | days | 1.7 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, I.J. Kang, J. Moroishi, Y. Shimasaki, and Y. Oshima | Pharmaceuticals and Personal Care Products Toxicity to Japanese Medaka Fish (Oryzias latipes) | J. Fac. Agric. Kyushu Univ.54(2): 407-411 | 2009 | 2018/03/19 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LOEC | 1 | days | 5 | ng/egg ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S.G. Kim, M. Seki, I.J. Kang, T. Hano, Y. Shimasaki, and Y. Oshima | In Ovo Nanoinjection of Triclosan, Diclofenac and Carbamazepine Affects Embryonic Development of Medaka Fish (Oryzias latipes) | Chemosphere79:966-973 | 2010 | 2018/03/19 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Physiological | LOEC | 4 | days | 1 | ng/egg ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S.G. Kim, M. Seki, I.J. Kang, T. Hano, Y. Shimasaki, and Y. Oshima | In Ovo Nanoinjection of Triclosan, Diclofenac and Carbamazepine Affects Embryonic Development of Medaka Fish (Oryzias latipes) | Chemosphere79:966-973 | 2010 | 2018/03/19 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Physiological | NOEC | 6 | days | 1 | ng/egg ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S.G. Kim, M. Seki, I.J. Kang, T. Hano, Y. Shimasaki, and Y. Oshima | In Ovo Nanoinjection of Triclosan, Diclofenac and Carbamazepine Affects Embryonic Development of Medaka Fish (Oryzias latipes) | Chemosphere79:966-973 | 2010 | 2018/03/19 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | NOEC | 1 | days | 1 | ng/egg ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S.G. Kim, M. Seki, I.J. Kang, T. Hano, Y. Shimasaki, and Y. Oshima | In Ovo Nanoinjection of Triclosan, Diclofenac and Carbamazepine Affects Embryonic Development of Medaka Fish (Oryzias latipes) | Chemosphere79:966-973 | 2010 | 2018/03/19 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 2000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, I.J. Kang, J. Moroishi, Y. Shimasaki, and Y. Oshima | Pharmaceuticals and Personal Care Products Toxicity to Japanese Medaka Fish (Oryzias latipes) | J. Fac. Agric. Kyushu Univ.54(2): 407-411 | 2009 | 2018/03/19 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 4 | days | 1700 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, I.J. Kang, J. Moroishi, Y. Shimasaki, and Y. Oshima | Pharmaceuticals and Personal Care Products Toxicity to Japanese Medaka Fish (Oryzias latipes) | J. Fac. Agric. Kyushu Univ.54(2): 407-411 | 2009 | 2018/03/19 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 4 | days | 399 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 23400 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 4 | days | 600 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kim,J.W., H. Ishibashi, R. Yamauchi, N. Ichikawa, Y. Takao, M. Hirano, M. Koga, and K. Arizono | Acute Toxicity of Pharmaceutical and Personal Care Products on Freshwater Crustacean (Thamnocephalus platyurus) and Fish (Oryzias latipes) | J. Toxicol. Sci.34(2): 227-232 | 2009 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 352 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Foran,C.M., E.R. Bennett, and W.H. Benson | Developmental Evaluation of a Potential Non-Steroidal Estrogen: Triclosan | Mar. Environ. Res.50:153-156 | 2000 | 2018/03/19 | |||||
魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 36200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | IC50 | 14 | days | 400 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2018/03/06 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | IC50 | 9 | days | 220 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 288 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | |||||
魚類 | Lepomis macrochirus (Bluegill) | Mortality | 1 | days | 1000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Reproduction | NOEC | 14 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 260 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 1 | days | >500 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mayer,F.L.,Jr., and M.R. Ellersieck | Manual of Acute Toxicity: Interpretation and Data Base for 410 Chemicals and 66 Species of Freshwater Animals | USDI Fish and Wildlife Service, Publication No.160, Washington, DC:505 p. | 1986 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Reproduction | NOEC | 14 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | NOEC | 14 | days | 156 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Enzyme | NOEC | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 360 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mayer,F.L.,Jr., and M.R. Ellersieck | Manual of Acute Toxicity: Interpretation and Data Base for 410 Chemicals and 66 Species of Freshwater Animals | USDI Fish and Wildlife Service, Publication No.160, Washington, DC:505 p. | 1986 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LOEC | 35 | days | 31.6 | μg/L | Unionized | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Behavior | NOEC | 5 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | 14 | days | 78.1 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2018/03/06 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Feeding behavior | NOEC | 5 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Morphology | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Growth | NOEC | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Morphology | NOEC | 21 | days | 75.2 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Reproduction | NOEC | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Growth | NOEC | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Behavior | NOEC | 7 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Feeding behavior | NOEC | 6 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Feeding behavior | NOEC | 7 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Feeding behavior | NOEC | 8 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | 9 | days | 125 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2018/03/06 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Feeding behavior | NOEC | 9 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Morphology | NOEL | 21 | days | 75.2 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Reproduction | NOEC | 7 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | 1 | days | 560 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 250 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | 14 | days | 630 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2018/03/06 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Reproduction | NOEC | 7 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | NOEL | 14 | days | 156 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Morphology | NOEL | 21 | days | 75.2 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Reproduction | NOEL | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Morphology | NOEL | 21 | days | 17.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Morphology | LOEL | 21 | days | 75.2 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Behavior | NOEC | 9 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Morphology | NOEL | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Growth | NOEC | 12 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Behavior | LOEC | 6 | days | 170 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nassef,M., S. Matsumoto, M. Seki, F. Khalil, I.J. Kang, Y. Shimasaki, Y. Oshima, and T. Honjo | Acute Effects of Triclosan, Diclofenac and Carbamazepine on Feeding Performance of Japanese Medaka Fish (Oryzias latipes) | Chemosphere80(9): 1095-1100 | 2010 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | NOEL | 4 | days | 100 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEC | 95 | days | 71.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | NOEC | 61 | days | 71.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 370 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Biochemical | NOEL | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | 9 | days | 500 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2018/03/06 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEL | 4 | days | 18000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | Mortality | NOEL | 4 | days | 18000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2018/03/06 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Population | NOEL | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Enzyme | NOEL | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | NOEL | 21 | days | 162.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | NOEC | 61 | days | 71.3 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Histological | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Morphology | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Biochemical | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEC | 35 | days | 34.1 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Orvos,D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan | Environ. Toxicol. Chem.21(7): 1338-1349 | 2002 | 2018/03/06 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Morphology | NOEC | 21 | days | 0.45 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 4 | days | 602 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2018/03/06 | |||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 400 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Tatarazako, N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms. | Environ.Sci. | 2004 | 2018/03/17 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 14 | days | 460 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | 環境庁 | 平成8年度 生態影響試験 | 1997 | 2018/03/06 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 220 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Tatarazako, N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms. | Environ.Sci. | 2004 | 2018/03/17 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 14 | days | 399 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Ishibashi, H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin. | Aquat.Toxicol. | 2004 | 2018/03/06 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | IC25 | 9 | days | 160 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2016/03/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | 21 | days | 0.17~0.45 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2016/03/25 | ||||||||
魚類 | Pimephales promelas (Fathead minnow) | Behavior | 12 | days | 0.17~0.45 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2016/03/25 | ||||||||
魚類 | Danio rerio (Zebrafish) | EC50 | 5 | days | 2.6589 | μM | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Padilla,S., D. Corum, B. Padnos, D.L. Hunter, A. Beam, K.A. Houck, N. Sipes, N. Kleinstreuer, T. Knudsen, D.J. Dix, and | Zebrafish Developmental Screening of the ToxCast Phase I Chemical Library | Reprod. Toxicol.33(2): 174-187 | 2012 | 2016/03/25 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | IC25 | 14 | days | 290 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tatarazako,N., H. Ishibashi, K. Teshima, K. Kishi, and K. Arizono | Effects of Triclosan on Various Aquatic Organisms | Environ. Sci.11(2): 133-140 | 2004 | 2016/03/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Behavior | 12 | days | 0.17~0.45 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2016/03/25 | ||||||||
魚類 | Oryzias latipes (Japanese medaka) | Growth | 21 | days | 17.3~162.1 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ishibashi,H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin | Aquat. Toxicol.67(2): 167-179 | 2004 | 2016/03/25 | ||||||||
魚類 | Danio rerio (Zebrafish) | EC10 | 5 | days | 2.2544 | μM | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Padilla,S., D. Corum, B. Padnos, D.L. Hunter, A. Beam, K.A. Houck, N. Sipes, N. Kleinstreuer, T. Knudsen, D.J. Dix, and | Zebrafish Developmental Screening of the ToxCast Phase I Chemical Library | Reprod. Toxicol.33(2): 174-187 | 2012 | 2016/03/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Behavior | 12 | days | 0.17~0.45 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schultz,M.M., S.E. Bartell, and H.L. Schoenfuss | Effects of Triclosan and Triclocarban, Two Ubiquitous Environmental Contaminants, on Anatomy, Physiology, and Behavior of the Fathead Minnow (Pimephales promelas) | Arch. Environ. Contam. Toxicol.63(1): 114-124 | 2012 | 2016/03/25 | ||||||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 0.54 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1990 | 2016/02/24 | ||||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 4.37 | mg/L | 12 ECHA Information on Registered Substances | 2 | study report | 1985 | 2016/02/24 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 0.26 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1990 | 2016/02/25 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | 600 | μg/L | 12 ECHA Information on Registered Substances | 2 | Kim et al. | 2009 | 2018/02/06 | |||||||
魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 370 | μg/L | 12 ECHA Information on Registered Substances | 2 | Orvos et al. | 2002 | 2018/03/03 | |||||||
魚類 | Danio rerio (Zebrafish) | fish embryo acute toxicity | LC50 | 96 | hours | 283 | μg/L | 12 ECHA Information on Registered Substances | 2 | Belanger et al. | 2013 | 2018/02/07 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | fish embryo acute toxicity | LC50 | 96 | hours | 399 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ishibashi et al. | 2004 | 2018/02/07 | |||||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 340 | μg/L | 12 ECHA Information on Registered Substances | 2 | Oliveira et al. | 2009 | 2018/02/06 | |||||||
魚類 | Danio rerio (Zebrafish) | fish embryo acute toxicity | LC50 | 96 | hours | 300 | μg/L | 12 ECHA Information on Registered Substances | 2 | Belanger et al. | 2014 | 2018/02/07 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | 210 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tamura et al. | 2013 | 2018/02/06 | |||||||
魚類 | Danio rerio (Zebrafish) | fish embryo acute toxicity | LC50 | 96 | hours | 420 | μg/L | 12 ECHA Information on Registered Substances | 2 | Oliveira et al. | 2009 | 2018/02/07 | |||||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 96 | hours | 540 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba-Geigy Ltd. | 1990 | 2018/02/06 | |||||||
魚類 | Danio rerio (Zebrafish) | mortality | EC50 | 96 | hours | 4370 | μg/L | 12 ECHA Information on Registered Substances | 1 | Ciba-Geigy | 1985 | 2018/03/03 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 260 | μg/L | 12 ECHA Information on Registered Substances | 2 | Procter & Gamble | 1990 | 2018/02/06 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 288 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | 1996 | 2018/02/21 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 0.25 | ppm | 3 USEPA Pesticide Ecotoxicity Database | J. Edwards | 1994 | 2018/02/21 | |||||||||
魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 36.2 | ppm | 3 USEPA Pesticide Ecotoxicity Database | C. Laird | 1990 | 2018/02/21 | |||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 23.4 | ppm | 3 USEPA Pesticide Ecotoxicity Database | C. Laird | 1990 | 2018/02/21 | |||||||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 0.67 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 352 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Foran, C.M., E.R. Bennett, and W.H. Benson | Developmental Evaluation of a Potential Non-Steroidal Estrogen: Triclosan. | Mar.Environ.Res. | 2000 | 2018/03/17 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | >360 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | D | Mayer, F.L.Jr., and M.R. Ellersieck | Manual of Acute Toxicity: Interpretation and Data Base for 410 Chemicals and 66 Species of Freshwater Animals. | Resour.Publ.No.160, U.S.Dep.Interior, Fish Wildl.Serv., Washington, DC | 1986 | 2018/03/17 | |||||
魚類 | Carassius auratus (Goldfish) | mortality | LC50 | 96 | hours | 1839 | μg/L | 12 ECHA Information on Registered Substances | 2 | Wang et al. | 2013 | 2018/02/06 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 48 | hours | 2.05 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Chemicals Investigation and Testing Institute. | Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan, ISBN 4-98074-101-1. | 1992 | 2016/02/08 | |||||||
魚類 | Brachydanio rerio (Zebrafish) | LC50 | 96 | hours | 540 | μg/L | 4 OECD SIDS (HPVC) | ECB | Environmental aspects of triclosan. | ECBI/18/02 Add. 22. Accessed at http://ecb.jrc.it/classlab/1802a22_IND_triclosan.pdf in April 2006. | 2004 | 2018/03/10 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | NOEC | 96 | hours | 100 | μg/L | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Acute toxicity of D1063.01 to Fathead Minnow (Pimephales promelas). | Analytical Bio-Chemistry Laboratories, Inc. Unpublished report, Project ID. 38655, Proctor & Gamble Company. | 1990 | 2018/03/10 | |||||||
魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 370 | μg/L | 4 OECD SIDS (HPVC) | Orvos DR, Versteeg DJ, Inauen J, Capdevielle M, Rothenstein A. and Cunningham V | Aquatic Toxicity of Triclosan. Environmental Toxicology and Chemistry | 2002 | 2018/03/10 | ||||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 360 | μg/L | 4 OECD SIDS (HPVC) | Mayer FLJ and Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 Chemicals and 66 Species of freshwater animal. | Resource Publication 160, US Department of Interior, US Fish and Wildlife Service, Washington, DC. | 1986 | 2018/03/10 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 4 | days | 670 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | 環境庁 | 平成8年度 生態影響試験 | 1997 | 2018/03/06 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 4 | days | 602 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Ishibashi, H., N. Matsumura, M. Hirano, M. Matsuoka, H. Shiratsuchi, Y. Ishibashi, Y. Takao, and K. Arizono | Effects of Triclosan on the Early Life Stages and Reproduction of Medaka Oryzias latipes and Induction of Hepatic Vitellogenin. | Aquat.Toxicol. | 2004 | 2018/03/17 | |||||
魚類 | Leuciscus idus (Orfe) | LC50 | 96 | hours | 560 | μg/L | 4 OECD SIDS (HPVC) | ECB | Environmental aspects of triclosan. | ECBI/18/02 Add. 22. Accessed at http://ecb.jrc.it/classlab/1802a22_IND_triclosan.pdf in April 2006. | 2004 | 2018/03/10 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 24 | hours | >500 | μg/L | 4 OECD SIDS (HPVC) | Mayer FLJ and Ellersieck MR | Manual of acute toxicity: Interpretation and data base for 410 Chemicals and 66 Species of freshwater animal. | Resource Publication 160, US Department of Interior, US Fish and Wildlife Service, Washington, DC. | 1986 | 2018/03/10 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | fish embryo acute toxicity | LC50 | 96 | hours | 190 | μg/L | 12 ECHA Information on Registered Substances | 2 | Fritsch et al. | 2013 | 2018/02/07 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | LC0 | 96 | hours | 0.32 | mg/L | 11 Japan チャレンジプログラム | 2018/03/12 | |||||||||||
魚類 | Oryzias latipes (Japanese medaka) | reproduction | LC50 | 96 | hours | 602 | μg/L | 4 OECD SIDS (HPVC) | Ishibashi H, Matsumura N, Hirano M, Matsuoka M, Shiratsuchi H, Ishibashi Y, Takao Y and Arizono K | Effects of triclosan on the early life stages and reproduction of medaka Oryzias latipes and induction of hepatic vitellogenin. | Aquatic Toxicology | 2004 | 2018/03/10 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 2 | days | 270 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||
魚類 | Oryzias latipes (Japanese medaka) | LC100 | 96 | hours | 1 | mg/L | 11 Japan チャレンジプログラム | 2018/03/12 | |||||||||||
魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 370 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 0.67 | mg/L | 11 Japan チャレンジプログラム | 2018/03/12 | |||||||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 260 | μg/L | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Acute toxicity of D1063.01 to Fathead Minnow (Pimephales promelas). | Analytical Bio-Chemistry Laboratories, Inc. Unpublished report, Project ID. 38655, Proctor & Gamble Company. | 1990 | 2018/03/10 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | survival | LC50 | 48 | hours | 352 | μg/L | 4 OECD SIDS (HPVC) | Foran CM, Bennett ER and Benson WH | Developmental evaluation of a potential non- steroidal estrogen: triclosan. | Marine Environmental Research | 2000 | 2018/03/10 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 260 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||
魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 2 | days | 410 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 350 | μg/L | 4 OECD SIDS (HPVC) | ECB | Environmental aspects of triclosan. | ECBI/18/02 Add. 22. Accessed at http://ecb.jrc.it/classlab/1802a22_IND_triclosan.pdf in April 2006. | 2004 | 2018/03/10 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | reproduction | LC50 | 96 | hours | 399 | μg/L | 4 OECD SIDS (HPVC) | Ishibashi H, Matsumura N, Hirano M, Matsuoka M, Shiratsuchi H, Ishibashi Y, Takao Y and Arizono K | Effects of triclosan on the early life stages and reproduction of medaka Oryzias latipes and induction of hepatic vitellogenin. | Aquatic Toxicology | 2004 | 2018/03/10 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 24 | hours | 360 | μg/L | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Acute toxicity of D1063.01 to Fathead Minnow (Pimephales promelas). | Analytical Bio-Chemistry Laboratories, Inc. Unpublished report, Project ID. 38655, Proctor & Gamble Company. | 1990 | 2018/03/10 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | fertility | NOEC | 21 | days | >=13.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2012 | 2016/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | fecundity | NOEC | 21 | days | >=13.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2012 | 2016/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEL | 96 | hours | 0.1 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1990 | 2016/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | plasma sex steroids (17beta-estradiol and testosterone) | NOEC | 21 | days | >=13.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2012 | 2016/02/25 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 96 | days | 14.1 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1996 | 2016/02/24 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | gonad-somatic index | NOEC | 21 | days | >=13.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2012 | 2016/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | secondary sexual characteristics | NOEC | 21 | days | >=13.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2012 | 2016/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | gonadal histology | NOEC | 21 | days | >=13.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2012 | 2016/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | adult behaviour | NOEC | 21 | days | >=13.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2012 | 2016/02/25 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LOEC | 96 | days | 71.3 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1996 | 2016/02/24 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | vitellogenin | NOEC | 21 | days | >=13.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2012 | 2016/02/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | adult mortality | NOEC | 21 | days | >=13.5 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2012 | 2016/02/25 | ||||||
魚類 | Danio rerio (Zebrafish) | NOEC | 9 | days | 29 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tamura et al. | 2012 | 2018/03/03 | ||||||||
魚類 | Danio rerio (Zebrafish) | EC10 | 9 | days | 150 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tatarazako et al. | 2004 | 2018/02/07 | ||||||||
魚類 | Pimephales promelas (Fathead minnow) | NOEC | 21 | days | >13.5 | μg/L | 12 ECHA Information on Registered Substances | 1 | BASF SE | Rep. No CSCH01-00222 | 2012 | 2018/02/07 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | hatching and the survival of juveniles | NOEC | 96 | days | 34.1 | μg/L | 12 ECHA Information on Registered Substances | 2 | Ciba Specialty Chemicals | Rep. no. 42726R | 1996 | 2018/02/07 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | 100 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | 1996 | 2018/02/21 | |||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | 18 | ppm | 3 USEPA Pesticide Ecotoxicity Database | C. Laird | 1990 | 2018/02/21 | |||||||||
魚類 | Lepomis macrochirus (Bluegill) | NOEL | 96 | hours | 18 | ppm | 3 USEPA Pesticide Ecotoxicity Database | C. Laird | 1990 | 2018/02/21 | |||||||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 14 | days | 0.46 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
魚類 | Oryzias latipes (Japanese medaka) | NOEC | 0.031 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||||
魚類 | Oryzias latipes (Japanese medaka) | LOEC | 0.063 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||||
魚類 | Oryzias latipes (Japanese medaka) | NOEC | 14 | days | 0.18 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成29年3月版) | 2018/02/19 | |||||||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 7 | days | 0.55 | mg/L | 11 Japan チャレンジプログラム | 2018/03/14 | |||||||||||
魚類 | Oryzias latipes (Japanese medaka) | NOEC | 14 | days | 0.18 | mg/L | 11 Japan チャレンジプログラム | 2018/03/12 | |||||||||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 14 | days | 0.46 | mg/L | 11 Japan チャレンジプログラム | 2018/03/12 | |||||||||||
魚類 | Oryzias latipes (Japanese medaka) | Growth | NOEC | 38 | days | 62.5 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | 環境省 | 平成13年度 生態影響試験 | 2002 | 2018/03/17 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEC | 15.1 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | NOEC | 34.1 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | Orvos, D.R., D.J. Versteeg, J. Inauen, M. Capdevielle, A. Rothenstein, and V. Cunningham | Aquatic Toxicity of Triclosan. | Environ.Toxicol.Chem. | 2002 | 2018/03/17 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | GSI of female of medaka | NOEC | 21 | days | <13 | μg/L | 4 OECD SIDS (HPVC) | Ishibashi H, Matsumura N, Hirano M, Matsuoka M, Shiratsuchi H, Ishibashi Y, Takao Y and Arizono K | Effects of triclosan on the early life stages and reproduction of medaka Oryzias latipes and induction of hepatic vitellogenin. | Aquatic Toxicology | 2004 | 2018/03/10 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | NOEC | 14 | days | 156 | μg/L | 4 OECD SIDS (HPVC) | Ishibashi H, Matsumura N, Hirano M, Matsuoka M, Shiratsuchi H, Ishibashi Y, Takao Y and Arizono K | Effects of triclosan on the early life stages and reproduction of medaka Oryzias latipes and induction of hepatic vitellogenin. | Aquatic Toxicology | 2004 | 2018/03/10 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | total length of female medaka | NOEC | 21 | days | 61 | 4 OECD SIDS (HPVC) | Ishibashi H, Matsumura N, Hirano M, Matsuoka M, Shiratsuchi H, Ishibashi Y, Takao Y and Arizono K | Effects of triclosan on the early life stages and reproduction of medaka Oryzias latipes and induction of hepatic vitellogenin. | Aquatic Toxicology | 2004 | 2018/03/10 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | EC10 | 14 | days | 160 | μg/L | 12 ECHA Information on Registered Substances | 2 | Tatarazako et al. | 2004 | 2018/02/07 | ||||||||
魚類 | Pimephales promelas (Fathead minnow) | NOEL | 96 | hours | 0.1 | ppm | 3 USEPA Pesticide Ecotoxicity Database | J. Edwards | 1994 | 2018/02/21 | |||||||||
魚類 | Brachydanio rerio (Zebrafish) | IC50 | 9 | days | 220 | μg/L | 4 OECD SIDS (HPVC) | Tatarazako N, Ishibashi H, Teshima K, Kishi K, Arizono K | Effects of triclosan on various aquatic organisms. | Environ Sciences | 2004 | 2018/03/10 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | LOEC | 14 | days | 0.32 | mg/L | 11 Japan チャレンジプログラム | 2018/03/14 | |||||||||||
魚類 | Oryzias latipes (Japanese medaka) | 毒性症状 | LOEC | 38 | days | 0.0625 | mg/L | 11 Japan チャレンジプログラム | 2018/03/14 | ||||||||||
魚類 | Brachydanio rerio (Zebrafish) | early life stage | NOEC | 10 | days | 200 | μg/L | 4 OECD SIDS (HPVC) | Ferrari B, Paxeus N, Pollio A, Andreozzi R, Marotta R, Vogna D, Lyberatos G, Garric J | Fate and effect of triclosan in the aquatic ecosystems: data for a risk assessment [poster]. | In: Society of Environmental Toxicology and Chemistry Annual Meeting in Europe; 2002 May 12 – 16; Vienna, Austria. Brussels (BE): SETAC Europe. | 2002 | 2018/03/11 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | 卵のふ化数及びふ化日数、発生異常数、ふ化後の生存数、毒性症状、生存した稚魚の体重及び体長 | NOEC | 38 | days | 0.0313 | mg/L | 11 Japan チャレンジプログラム | 2018/03/12 | ||||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | early life stage | NOEC | 96 | days | 34.1 | μg/L | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Early life-stage toxicity of triclosan to Rainbow Trout (Oncorhynchus mykiss) under flow through conditions. | Analytical Bio-Chemistry Laboratories, Inc. Unpublished study No. 42726R, Unilever Research, NJ, USA. | 1996 | 2018/03/11 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | HIS of female | NOEC | 21 | days | <13 | μg/L | 4 OECD SIDS (HPVC) | Ishibashi H, Matsumura N, Hirano M, Matsuoka M, Shiratsuchi H, Ishibashi Y, Takao Y and Arizono K | Effects of triclosan on the early life stages and reproduction of medaka Oryzias latipes and induction of hepatic vitellogenin. | Aquatic Toxicology | 2004 | 2018/03/10 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | early life stage | LOEC | 96 | days | 71.3 | μg/L | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Early life-stage toxicity of triclosan to Rainbow Trout (Oncorhynchus mykiss) under flow through conditions. | Analytical Bio-Chemistry Laboratories, Inc. Unpublished study No. 42726R, Unilever Research, NJ, USA. | 1996 | 2018/03/11 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | IC50 | 14 | days | 400 | μg/L | 4 OECD SIDS (HPVC) | Tatarazako N, Ishibashi H, Teshima K, Kishi K, Arizono K | Effects of triclosan on various aquatic organisms. | Environ Sciences | 2004 | 2018/03/10 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | early life stage | 96 | days | 49.3 | μg/L | 4 OECD SIDS (HPVC) | ABC Laboratories Inc. | Early life-stage toxicity of triclosan to Rainbow Trout (Oncorhynchus mykiss) under flow through conditions. | Analytical Bio-Chemistry Laboratories, Inc. Unpublished study No. 42726R, Unilever Research, NJ, USA. | 1996 | 2018/03/11 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | VTG of male | NOEC | 21 | days | 13 | μg/L | 4 OECD SIDS (HPVC) | Ishibashi H, Matsumura N, Hirano M, Matsuoka M, Shiratsuchi H, Ishibashi Y, Takao Y and Arizono K | Effects of triclosan on the early life stages and reproduction of medaka Oryzias latipes and induction of hepatic vitellogenin. | Aquatic Toxicology | 2004 | 2018/03/10 |