【注意事項】
* 化学物質有害性情報データベース情報更新日が2019年9月以前はRead-acrossデータでも○としていないので、毒性値の取り扱いには注意が必要である。
| 生物種 | 学名 | 影響内容 | エンドポイント | 暴露期間(値) | 暴露期間(単位) | 毒性値 | 毒性値(単位) | Read-across * | QSAR | GLP | 設定濃度 | 実測濃度 | 情報源 | 情報源による信頼性評価 | 著者 | タイトル | 記載誌 | 発行年 | 情報更新日 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| subject type | scientific name | effect | endpoint | exposure duration value | exposure duration unit | toxicity value | toxicity unit | Read-across | QSAR | GLP | nominal concentration | measured concentration | original work type | original work reliability rank | author | title | referenced journal | publication year | Information update date |
| 藻類 | Scenedesmus acutus | MortalityMortality | 3 | days | 10000 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Krishnakumari,M.K. | Sensitivity of the Alga Scenedesmus acutus to Some Pesticides | Life Sci.20 | 1977 | ||||||||
| 藻類 | others Chlorella pyrenoidosa | Growth (Growth, general) | EC50 | 4 | days | 1 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3): 145-164 | 1985 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population (Abundance) | EC50 | 5 | days | 0.14 | mg/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 | 2019/02/13 | ||||||
| 藻類 | others Scenedesmus acutus | Mortality | 3 | days | 10 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Krishnakumari,M.K. | Sensitivity of the Alga Scenedesmus acutus to Some Pesticides | Life Sci.20:1525-1532 | 1977 | 2019/02/13 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | Population (Abundance) | NOEL | 5 | days | <0.057 | mg/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 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population (Abundance) | EC50 | 5 | days | 0.045 | mg/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 | 2019/02/13 | ||||||
| 藻類 | others Nannochloropsis oculata | Population (Population growth rate) | EC50 | 1 | days | 0.04 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2019/02/13 | ||||||
| 藻類 | others Nannochloropsis oculata | Population (Population growth rate) | EC50 | 2 | days | 0.04 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2019/02/13 | ||||||
| 藻類 | others Chlorella pyrenoidosa | Growth (Growth, general) | EC50 | 0.16 | days | 1 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3): 145-164 | 1985 | 2019/02/13 | ||||||
| 藻類 | others Haematococcus pluvialis | Population (Population changes, general) | EC10 | >6 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knie,J., A. Halke, I. Juhnke, and W. Schiller | Results of Studies on Chemical Substances with Four Biotests (Ergebnisse der Untersuch-Ungen von Chemischen Stoffen mit vier Biotests) | Dtsch. Gewaesserkd. Mitt.27(3): 77-79 | 1983 | 2019/02/13 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass (area under growth curve method) | LOEC | 72 | hours | 0.1 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | 生長阻害 | NOECr | 72 | hours | 4.3 | μg/L | 2 日本環境省 農薬登録保留基準（水産動植物） | 2018/12/18 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | 生長阻害 | ErC50 | 72 | hours | 16.7 | μg/L | 2 日本環境省 農薬登録保留基準（水産動植物） | 2018/12/18 | ||||||||||
| 藻類 | Chlorella vulgaris | IC50 | 72 | hours | 5.5 | mg/L | 4 OECD SIDS (HPVC) | 3 | Jouany JM, Truhaut R, Vasseur P, Klein D, Ferard JF and Deschamps P | An example of interaction between environmental pollutants: Modification of thiram toxicity to freshwater organisms by nitrites or nitrates in relation to nitrosamine synthesis | Ecotoxicology and environmental safety | 1985 | 2018/12/06 | ||||||
| 藻類 | others Nannochloropsis oculata | Population (Population growth rate) | EC50 | 3 | days | 0.04 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2019/02/13 | ||||||
| 藻類 | Chlorella vulgaris | Growth (Growth, general) | EC50 | 3 | days | 5.5 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3): 327-338 | 1985 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass (area under growth curve method) | LOEC | 72 | hours | 0.03 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | LOEC | 72 | hours | 0.1 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 0.03 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | biomass (area under growth curve method) | EC50 | 72 | hours | 0.06 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.19 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | biomass (area under growth curve method) | LOEC | 72 | hours | 0.03 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | LOEC | 72 | hours | 0.1 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.19 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | biomass (area under growth curve method) | LOEC | 72 | hours | 0.1 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Chlorella vulgaris | IC50 | 72 | hours | 5.5 | mg/L | 4 OECD SIDS (HPVC) | 3 | Jouany JM, Truhaut R, Vasseur P, Klein D, Ferard JF and Deschamps P | An example of interaction between environmental pollutants: Modification of thiram toxicity to freshwater organisms by nitrites or nitrates in relation to nitrosamine synthesis | Ecotoxicology and environmental safety | 1985 | 2018/12/06 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass (area under growth curve method) | EC50 | 72 | hours | 0.06 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 0.03 | mg/L [Conc. based on: test mat.] | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2018/12/06 | |||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 140 | 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 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 5 | days | 45 | 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 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Population | NOEL | 5 | days | <57 | 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 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Growth | EC50 | 3 | days | 5500 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3): 327-338 | 1985 | 2016/03/25 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 120 | hours | 0.076 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1993 | 2020/03/04 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 0.065 | mg/L | ○ | 0.0125, 0.025, 0.050, 0.10, 0.20, 0.40 mg/L | 0.0057, 0.0083, 0.016, 0.035, 0,065, 0.12 mg/L (geometric means) | 12 ECHA Information on Registered Substances | 1 | study report | 1993 | |||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 24 | hours | 0.12 | mg/L | ○ | 0.0125, 0.025, 0.050, 0.10, 0.20, 0.40 mg/L | 0.0057, 0.0083, 0.016, 0.035, 0,065, 0.12 mg/L (geometric means) | 12 ECHA Information on Registered Substances | 1 | study report | 1993 | |||||
| 藻類 | Pseudokirchneriella subcapitata | PopulationAbundance | EC50 EC50 | 5 | days | 0.045 | ppm [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 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | PopulationAbundance | NOEL NOEL | 5 | days | <0.057 | ppm [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 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | PopulationAbundance | EC50 EC50 | 5 | days | 0.14 | ppm [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 | |||||||
| 藻類 | Chlorella pyrenoidosa | GrowthGrowth, general | EC50 EC50/ | 96 | hours | 1000 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3) | 1985 | |||||||
| 藻類 | Chlorella pyrenoidosa | GrowthGrowth, general | EC50 EC50/ | 4 | hours | 1000 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3) | 1985 | |||||||
| 藻類 | Chlorella vulgaris | GrowthGrowth, general | EC50 EC50 | 72 | hours | 5500 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3) | 1985 | |||||||
| 藻類 | Chlorella sp. Chlorella pyrenoidosa | breakdown products | EC50 | 96 | hours | 1 | mg/L | 10 EHC (Environmental Health Criteria) | VAN LEEUWEN, C.J. | Ecotoxicological aspects of dithiocarbamates | Utrecht, University of Utrecht (Thesis). | 1986 | 2018/12/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | EC50 | 5 | days | 45 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | Huntingdon Research Center, England | 1992 | 2019/02/27 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | EC50 | 5 | days | 140 | ppb | 3 USEPA Pesticide Ecotoxicity Database | J. Edwards | Huntingdon Research Center, England | 1992 | 2019/02/27 | ||||||||
| 藻類 | Chlorella sp. Chlorella pyrenoidosa | Growth | EC50 | 4 | days | 1000 | 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 | Van Leeuwen, C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests. | Aquat.Toxicol. | 1985 | 2016/03/07 | |||||
| 藻類 | Chlorella sp. Chlorella pyrenoidosa | Biomass | EC50 | 4 | days | 320 | 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 | Van Leeuwen, C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests. | Aquat.Toxicol. | 1985 | 2016/03/07 | |||||
| 藻類 | Scenedesmus sp. Scenedesmus acutus | Growth | EC50 | 5 | days | 5000 | 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 | Krishnakumari, M.K. | Sensitivity of the Alga Scenedesmus acutus to Some Pesticides. | Life Sci. | 1977 | 2016/03/07 | |||||
| 藻類 | Anabaena sp. | EC50 | 14 | 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） | b | Cameron, H.J., and G.R. Julian | The Effects of Four Commonly used Fungicides on the Growth of Cyanobacteria. | Plant Soil | 1984 | 2016/03/07 | ||||||
| 藻類 | Chlorella vulgaris | Growth | IC50 | 3 | days | 5500 | 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 | Jouany, J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in. | Ecotoxicol.Environ.Saf. | 1985 | 2016/03/07 | |||||
| 藻類 | Anabaena sp. | EC50 | 14 | days | 60 | 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 | Cameron, H.J., and G.R. Julian | The Effects of Four Commonly used Fungicides on the Growth of Cyanobacteria. | Plant Soil | 1984 | 2016/03/07 | ||||||
| 藻類 | Chlorella sp. Chlorella pyrenoidosa | EC50 | 96 | hours | 1 | mg/L | 10 EHC (Environmental Health Criteria) | VAN LEEUWEN, C.J. | Ecotoxicological aspects of dithiocarbamates | Utrecht, University of Utrecht (Thesis) | 2016/03/06 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | 生長阻害 | NOECr | 72 | hours | 4.3 | μg/L | 2 日本環境省 農薬登録保留基準（水産動植物） | 環境省 | 水産動植物の被害防止に係る農薬登録保留基準の設定に関する資料 | 2016/02/17 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 0.06 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2016/02/22 | |||||
| 藻類 | Chlorella vulgaris | IC50 | 72 | hours | 5.5 | mg/L | 4 OECD SIDS (HPVC) | 3 | Jouany JM, Truhaut R, Vasseur P, Klein D, Ferard JF and Deschamps P | An example of interaction between environmental pollutants: Modification of thiram toxicity to freshwater organisms by nitrites or nitrates in relation to nitrosamine synthesis | Ecotoxicology and environmental safety | 2008 | 2016/02/22 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | 生長阻害 | ErC50 | 72 | hours | 16.7 | μg/L | 2 日本環境省 農薬登録保留基準（水産動植物） | 環境省 | 水産動植物の被害防止に係る農薬登録保留基準の設定に関する資料 | 2016/02/17 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.19 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2016/02/22 | |||||
| 藻類 | Selenastrum capricornutum | EC50 | 5 | days | 45 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | 1993 | 2016/02/02 | |||||||||
| 藻類 | Selenastrum capricornutum | EC50 | 5 | days | 140 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | J. Edwards | 1998 | 2016/02/02 | |||||||||
| 藻類 | Selenastrum capricornutum | biomass | EC50 | 120 | hours | 0.076 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1993 | 2016/03/18 | ||||||
| 藻類 | Selenastrum capricornutum | biomass | EC50 | 72 | hours | 0.065 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1993 | 2016/03/18 | ||||||
| 藻類 | Selenastrum capricornutum | growth rate | EC50 | 24 | hours | 0.12 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1993 | 2016/03/18 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | NOEL | 5 | days | <57 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | Huntingdon Research Center, England | 1992 | 2019/02/27 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | LOEC | 72 | hours | 0.1 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2016/02/22 | |||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | LOEC | 72 | hours | 0.03 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2016/02/22 | |||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 0.03 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2016/02/22 | |||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | LOEC | 72 | hours | 0.1 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Growth inhibition test of Bis (dimethylthiocarbamoyl) disulfide on fresh water alga | 2008 | 2016/02/22 | |||||
| 藻類 | Selenastrum capricornutum | NOEL | 5 | days | 57 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | 1993 | 2016/02/02 | |||||||||
| 甲殻類 | Daphnia magna | PhysiologyOxygen consumption | LOEL LOEL | 210 | 9 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J.C., M.L. Saker, L.F. Oliva Teles, and V.M. Vasconcelos | Oxygen Consumption by Daphnia magna Straus as a Marker of Chemical Stress in the Aquatic Environment | Environ. Toxicol. Chem.26(9) | 2007 | ||||||||
| 甲殻類 | Daphnia magna | BehaviorDistance moved, change in direct movement | EC50 EC50 | 0.006 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knie,J., A. Halke, I. Juhnke, and W. Schiller | Results of Studies on Chemical Substances with Four Biotests (Ergebnisse der Untersuch-Ungen von Chemischen Stoffen mit vier Biotests) | Dtsch. Gewaesserkd. Mitt.27(3) | 1983 | |||||||||
| 甲殻類 | Daphnia magna | MortalityMortality | 210 | 9 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J.C., M.L. Saker, L.F. Oliva Teles, and V.M. Vasconcelos | Oxygen Consumption by Daphnia magna Straus as a Marker of Chemical Stress in the Aquatic Environment | Environ. Toxicol. Chem.26(9) | 2007 | |||||||||
| 甲殻類 | Daphnia magna | PhysiologyOxygen consumption | NOEL NOEL | 15 | 9 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J.C., M.L. Saker, L.F. Oliva Teles, and V.M. Vasconcelos | Oxygen Consumption by Daphnia magna Straus as a Marker of Chemical Stress in the Aquatic Environment | Environ. Toxicol. Chem.26(9) | 2007 | ||||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 4 | days | 0.225 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 3 | days | 0.4 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Asellus aquaticus | Mortality | LC50 | 4 | days | 61 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 2 | days | 0.48 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 3 | days | 0.13 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 3 | days | 0.2 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 4 | days | 0.06 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 3 | days | 0.41 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Behavior (Phototactic response) | LOEC | 2 | days | 0.075 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3): 417-422 | 2007 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Behavior (Phototactic response) | LOEC | 1 | days | 0.00938 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3): 417-422 | 2007 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 0.209392 | その他others [mol/L] | 17 Aquatic OASIS (OECD QSAR Toolbox) | Peter C. von der Ohe, Ralph Kühne, Ralf-Uwe Ebert, Rolf Altenburger, Matthias Liess, and Gerrit Schüürmann | Structural Alerts-A New Classification Model to Discriminate Excess Toxicity from Narcotic Effect Levels of Organic Compounds in the Acute Daphnid Assay | Chem. Res. Toxicol., 18 (3) | 2005 | 2019/02/22 | ||||||
| 甲殻類 | Daphnia magna | Intoxication | EC50 | 48 | hours | 0.186621 | その他others [mol/L] | 17 Aquatic OASIS (OECD QSAR Toolbox) | Furusjö, E., Andersson, M., Rahmberg, M., Svenson, A. | Estimating environmentally important properties of chemicals from the chemical structure | Estimating environmentally important properties of chemicals from the chemical structure - IVL Rapport B1517 | 2003 | 2019/02/22 | ||||||
| 甲殻類 | Daphnia magna | Behavior (Phototactic response) | LOEC | 0.14 | days | 0.3 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3): 417-422 | 2007 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 1 | days | 1 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3): 327-338 | 1985 | 2019/02/13 | |||||||
| 甲殻類 | others Americamysis bahia | Mortality | NOEL | 4 | days | 0.0023 | mg/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 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Physiology (Oxygen consumption) | LOEL | 0.14 | days | 0.009 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J.C., M.L. Saker, L.F. Oliva Teles, and V.M. Vasconcelos | Oxygen Consumption by Daphnia magna Straus as a Marker of Chemical Stress in the Aquatic Environment | Environ. Toxicol. Chem.26(9): 1987-1991 | 2007 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Behavior (Phototactic response) | NOEC | 0.14 | days | 0.15 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3): 417-422 | 2007 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Behavior (Phototactic response) | NOEC | 2 | days | 0.0375 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3): 417-422 | 2007 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Physiology (Oxygen consumption) | NOEL | 0.01 | days | 0.009 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J.C., M.L. Saker, L.F. Oliva Teles, and V.M. Vasconcelos | Oxygen Consumption by Daphnia magna Straus as a Marker of Chemical Stress in the Aquatic Environment | Environ. Toxicol. Chem.26(9): 1987-1991 | 2007 | 2019/02/13 | ||||||
| 甲殻類 | others Asellus aquaticus | Mortality | LC50 | 2 | days | 688 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 甲殻類 | others Artemia franciscana | Mortality | LC50 | 2 | days | 0.02 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2019/02/13 | ||||||
| 甲殻類 | others Americamysis bahia | Mortality | LC50 | 4 | days | 0.00336 | mg/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 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 21 | days | 0.008 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., F. Moberts, and G. Niebeek | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. II. Effects on Survival, Reproduction and Growth of Daphnia magna | Aquat. Toxicol.7:165-175 | 1988 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 0.21 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3): 145-164 | 1985 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 0.01 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 0.03 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Feeding behavior (Food consumption) | EC50 | 0.04 | days | 0.279 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fochtman,P., A. Raszka, and E. Nierzedska | The Use of Conventional Bioassays, Microbiotests, and Some "Rapid" Methods in the Selection of an Optimal Test Battery for the Assessment of Pesticides Toxicity | Environ. Toxicol.15(5): 376-384 | 2000 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Enzyme(s) (beta-Galactosidase) | EC50 | 0.04 | days | 0.00109 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fochtman,P., A. Raszka, and E. Nierzedska | The Use of Conventional Bioassays, Microbiotests, and Some "Rapid" Methods in the Selection of an Optimal Test Battery for the Assessment of Pesticides Toxicity | Environ. Toxicol.15(5): 376-384 | 2000 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 2 | days | 1.21 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Asellus aquaticus | Mortality | LC50 | 1 | days | 1882 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 甲殻類 | others Procambarus clarkii | Mortality | LC50 | 4 | days | 4.3 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Cheah,M.L., J.W.,Jr. Avault, and J.B. Graves | Acute Toxicity of Selected Rice Pesticides to Crayfish Procambarus clarkii | Prog. Fish-Cult.42(3): 169-172 | 1980 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1.08 | days | 1.3 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Frear,D.E.H., and J.E. Boyd | Use of Daphnia magna for the Microbioassay of Pesticides. I. Development of Standardized Techniques for Rearing Daphnia and Preparation of Dosage-Mortality Curves for Pesticides | J. Econ. Entomol.60(5): 1228-1236 | 1967 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 4 | days | 0.195 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 4 | days | 0.13 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 1 | days | 13.99 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Artemia franciscana | Mortality | LC50 | 1 | days | 0.13 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2019/02/13 | ||||||
| 甲殻類 | others Asellus aquaticus | Mortality | LC50 | 3 | days | 161 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 2 | days | 0.87 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Behavior (Distance moved, change in direct movement) | EC50 | 0.000006 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knie,J., A. Halke, I. Juhnke, and W. Schiller | Results of Studies on Chemical Substances with Four Biotests (Ergebnisse der Untersuch-Ungen von Chemischen Stoffen mit vier Biotests) | Dtsch. Gewaesserkd. Mitt.27(3): 77-79 | 1983 | 2019/02/13 | ||||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 1 | days | 1.37 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 1 | days | 4.77 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 2 | days | 0.36 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 1 | days | 3.26 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bluzat,R., O. Jonot, and J. Seuge | Acute Toxicity of a Fungicide, Thirame (Dithiocarbamate) in the Freshwater Amphipodal Crustacean Gammarus pulex | Environ. Pollut. A.29(3): 225-233 | 1982 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 0.14 | days | 0.009 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J.C., M.L. Saker, L.F. Oliva Teles, and V.M. Vasconcelos | Oxygen Consumption by Daphnia magna Straus as a Marker of Chemical Stress in the Aquatic Environment | Environ. Toxicol. Chem.26(9): 1987-1991 | 2007 | 2019/02/13 | |||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 210 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3): 145-164 | 1985 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 1 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3): 327-338 | 1985 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 30 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Physiology | NOEL | 0.25 | hours | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J.C., M.L. Saker, L.F. Oliva Teles, and V.M. Vasconcelos | Oxygen Consumption by Daphnia magna Straus as a Marker of Chemical Stress in the Aquatic Environment | Environ. Toxicol. Chem.26(9): 1987-1991 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | 3.5 | hours | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J.C., M.L. Saker, L.F. Oliva Teles, and V.M. Vasconcelos | Oxygen Consumption by Daphnia magna Straus as a Marker of Chemical Stress in the Aquatic Environment | Environ. Toxicol. Chem.26(9): 1987-1991 | 2007 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Mortality | 1 | days | 1000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3): 327-338 | 1985 | 2016/03/25 | |||||||
| 甲殻類 | Daphnia magna | Physiology | LOEL | 3.5 | hours | 9 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J.C., M.L. Saker, L.F. Oliva Teles, and V.M. Vasconcelos | Oxygen Consumption by Daphnia magna Straus as a Marker of Chemical Stress in the Aquatic Environment | Environ. Toxicol. Chem.26(9): 1987-1991 | 2007 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 10 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 1.08 | days | 1300 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Frear,D.E.H., and J.E. Boyd | Use of Daphnia magna for the Microbioassay of Pesticides. I. Development of Standardized Techniques for Rearing Daphnia and Preparation of Dosage-Mortality Curves for Pesticides | J. Econ. Entomol.60(5): 1228-1236 | 1967 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Biochemical | EC50 | 1 | hours | 1.09 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fochtman,P., A. Raszka, and E. Nierzedska | The Use of Conventional Bioassays, Microbiotests, and Some "Rapid" Methods in the Selection of an Optimal Test Battery for the Assessment of Pesticides Toxicity | Environ. Toxicol.15(5): 376-384 | 2000 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | EC50 | 1 | hours | 279 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fochtman,P., A. Raszka, and E. Nierzedska | The Use of Conventional Bioassays, Microbiotests, and Some "Rapid" Methods in the Selection of an Optimal Test Battery for the Assessment of Pesticides Toxicity | Environ. Toxicol.15(5): 376-384 | 2000 | 2016/03/25 | ||||||
| 甲殻類 | Daphnia magna | Behavior | EC50 | 0.006 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Knie,J., A. Halke, I. Juhnke, and W. Schiller | Results of Studies on Chemical Substances with Four Biotests (Ergebnisse der Untersuch-Ungen von Chemischen Stoffen mit vier Biotests) | Dtsch. Gewaesserkd. Mitt.27(3): 77-79 | 1983 | 2016/03/25 | ||||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 21 | days | 8 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., F. Moberts, and G. Niebeek | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. II. Effects on Survival, Reproduction and Growth of Daphnia magna | Aquat. Toxicol.7:165-175 | 1988 | 2016/03/25 | ||||||
| 甲殻類 | Intoxication | EC50 | 48 | hours | 0.000776 | mmol/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Furusjö, E., Andersson, M., Rahmberg, M., Svenson, A. | Estimating environmentally important properties of chemicals from the chemical structure | Estimating environmentally important properties of chemicals from the chemical structure - IVL Rapport B1517 | 2003 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC100 | 48 | hours | 1.3 | mg/L | ○ | control, 0.046, 0.10, 0.22, 0.46, 1.0 mg/L | 0h:128 – 203% of nominal 48h: 83 – 132% of nominal | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Daphnia magna | mobility | NOEC | 48 | hours | 0.14 | mg/L | ○ | control, 0.046, 0.10, 0.22, 0.46, 1.0 mg/L | 0h:128 – 203% of nominal 48h: 83 – 132% of nominal | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.38 | mg/L | ○ | control, 0.046, 0.10, 0.22, 0.46, 1.0 mg/L | 0h:128 – 203% of nominal 48h: 83 – 132% of nominal | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 11 | μg/L | ○ | 1.0, 2.0, 4.0, 8.0, 16, 32, 64 µg/L | 0h: 25 – 93% of nominal 48h: 0 – 43% of nominal | 12 ECHA Information on Registered Substances | 2 | study report | 1994 | |||||
| 甲殻類 | Mortality | LC50 | 48 | hours | 0.000871 | mmol/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Peter C. von der Ohe, Ralph Kühne, Ralf-Uwe Ebert, Rolf Altenburger, Matthias Liess, and Gerrit Schüürmann | Structural Alerts-A New Classification Model to Discriminate Excess Toxicity from Narcotic Effect Levels of Organic Compounds in the Acute Daphnid Assay | Chem. Res. Toxicol., 18 (3) | 2005 | 2020/03/18 | |||||||
| 甲殻類 | Daphnia magna | other: mortality and mobility | LC50 | 48 | hours | >0.2 | × | 12 ECHA Information on Registered Substances | study report | 2008 | |||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 26 | μg/L | ○ | 1.0, 2.0, 4.0, 8.0, 16, 32, 64 µg/L | 0h: 25 – 93% of nominal 48h: 0 – 43% of nominal | 12 ECHA Information on Registered Substances | 2 | study report | 1994 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | >0.1 | × | 0.1, 0.2 ,0.4, 0.8, 1.6 mg/L | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.18 | mg/L | × | 0.1, 0.2 ,0.4, 0.8, 1.6 mg/L | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | ||||||
| 甲殻類 | Daphnia magna | BehaviorPhototactic response | LOEC LOEC | 3.5 | hours | 300 | μg/L [Formulation] | 0 ug/L / 9.38 ug/L / 18.75 ug/L / 37.50 ug/L / 75.00 ug/L / 150.00 ug/L / 300.00 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3) | 2007 | ||||||
| 甲殻類 | Crassostrea gigas | IntoxicationImmobile | NOEL NOEL | 48 | hours | <1.3 | ppb [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 | |||||||
| 甲殻類 | Crassostrea gigas | IntoxicationImmobile | EC50 EC50 | 48 | hours | 4.7 | ppb [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 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | 24 | hours | 1000 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3) | 1985 | ||||||||
| 甲殻類 | Americamysis bahia | MortalityMortality | NOEL NOEL | 96 | hours | 2.3 | ppb [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 | |||||||
| 甲殻類 | Daphnia magna | BehaviorPhototactic response | NOEC NOEC | 3.5 | hours | 150 | μg/L [Formulation] | 0 ug/L / 9.38 ug/L / 18.75 ug/L / 37.50 ug/L / 75.00 ug/L / 150.00 ug/L / 300.00 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3) | 2007 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 210 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3) | 1985 | |||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 1 | hours | 0.279 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fochtman,P., A. Raszka, and E. Nierzedska | The Use of Conventional Bioassays, Microbiotests, and Some "Rapid" Methods in the Selection of an Optimal Test Battery for the Assessment of Pesticides Toxicity | Environ. Toxicol.15(5) | 2000 | |||||||
| 甲殻類 | Daphnia magna | BehaviorPhototactic response | LOEC LOEC | 24 | hours | 9.38 | μg/L [Formulation] | 0 ug/L / 9.38 ug/L / 18.75 ug/L / 37.50 ug/L / 75.00 ug/L / 150.00 ug/L / 300.00 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3) | 2007 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50*/ | 26 | hours | 1300 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Frear,D.E.H., and J.E. Boyd | Use of Daphnia magna for the Microbioassay of Pesticides. I. Development of Standardized Techniques for Rearing Daphnia and Preparation of Dosage-Mortality Curves for Pesticides | J. Econ. Entomol.60(5) | 1967 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 0.01 | mg/L [Formulation] | 0 mg/L / 0.005-0.5 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3) | 2009 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 24 | hours | 0.03 | mg/L [Formulation] | 0 mg/L / 0.005-0.5 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3) | 2009 | ||||||
| 甲殻類 | Americamysis bahia | MortalityMortality | LC50 LC50 | 96 | hours | 3.36 | ppb [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 | |||||||
| 甲殻類 | Daphnia magna | BehaviorPhototactic response | LOEC LOEC | 48 | hours | 75 | μg/L [Formulation] | 0 ug/L / 9.38 ug/L / 18.75 ug/L / 37.50 ug/L / 75.00 ug/L / 150.00 ug/L / 300.00 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3) | 2007 | ||||||
| 甲殻類 | Daphnia magna | BehaviorPhototactic response | NOEC NOEC | 48 | hours | 37.5 | μg/L [Formulation] | 0 ug/L / 9.38 ug/L / 18.75 ug/L / 37.50 ug/L / 75.00 ug/L / 150.00 ug/L / 300.00 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Martins,J., M.L. Soares, M.L. Saker, L. OlivaTeles, and V.M. Vasconcelos | Phototactic Behavior in Daphnia magna Straus as an Indicator of Toxicants in the Aquatic Environment | Ecotoxicol. Environ. Saf.67(3) | 2007 | ||||||
| 甲殻類 | Crassostrea gigas | EC50 | 48 | hours | 4.7 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | ICI Plant Protection Division, England | 1992 | 2019/02/27 | ||||||||
| 甲殻類 | Mysidopsis bahia | LC50 | 96 | hours | 3.36 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | ICI Plant Protection Division, England | 1992 | 2019/02/27 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 0.108 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | mobility | NOEC | 24 | hours | 0.027 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | LOEC | 24 | hours | 0.045 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.036 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | mobility | LOEC | 48 | hours | 0.027 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | 遊泳阻害 | 48 | hours | 250 | μg/L | 2 日本環境省 農薬登録保留基準（水産動植物） | 2018/12/18 | |||||||||||
| 甲殻類 | Mysidopsis bahia | LC50 | 96 | hours | 2.3 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | ICI Plant Protection Division, England | 1992 | 2019/02/27 | ||||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 0.21 | mg/L | 4 OECD SIDS (HPVC) | 3 | Van Leeuwen CJ, Maas-Diepeveen JL, Niebeek G, Vergouwm WHA, Griffioen PS and Luijken MW | Aquatic toxicological aspects of dithiocarbamates and related compounds. I. Short-term toxicity test | Aquatic toxicology | 1985 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | breakdown products | LC50 | 48 | hours | 0.21 | mg/L | 10 EHC (Environmental Health Criteria) | VAN LEEUWEN, C.J. | Ecotoxicological aspects of dithiocarbamates | Utrecht, University of Utrecht (Thesis). | 1986 | 2018/12/13 | ||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 0.21 | mg/L | 4 OECD SIDS (HPVC) | 3 | Van Leeuwen CJ, Maas-Diepeveen JL, Niebeek G, Vergouwm WHA, Griffioen PS and Luijken MW | Aquatic toxicological aspects of dithiocarbamates and related compounds. I. Short-term toxicity test | Aquatic toxicology | 1985 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 0.108 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | mobility | NOEC | 24 | hours | 0.027 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | LOEC | 24 | hours | 0.045 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | |||||||
| 甲殻類 | Daphnia magna | mobility | LOEC | 48 | hours | 0.027 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.036 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 0.21 | mg/L | 10 EHC (Environmental Health Criteria) | VAN LEEUWEN, C.J. | Ecotoxicological aspects of dithiocarbamates | Utrecht, University of Utrecht (Thesis) | 2016/03/06 | ||||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 210 | 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 | Van Leeuwen, C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests. | Aquat.Toxicol. | 1985 | 2016/03/07 | |||||
| 甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 48 | hours | 250 | μg/L | 2 日本環境省 農薬登録保留基準（水産動植物） | 環境省 | 水産動植物の被害防止に係る農薬登録保留基準の設定に関する資料 | 2016/02/17 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.036 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2016/02/22 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 0.108 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2016/02/22 | ||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 0.21 | mg/L | 4 OECD SIDS (HPVC) | 3 | Van Leeuwen CJ, Maas-Diepeveen JL, Niebeek G, Vergouwm WHA, Griffioen PS and Luijken MW | Aquatic toxicological aspects of dithiocarbamates and related compounds. I. Short-term toxicity test | Aquatic toxicology | 1985 | 2016/02/22 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.18 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | Unnamed | 1999 | 2019/02/20 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | >0.1 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | Unnamed | 1999 | 2019/02/20 | |||||
| 甲殻類 | Daphnia magna | Intoxication | ET50 | 48 | hours | 0.187 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Furusjö, E., Andersson, M., Rahmberg, M., Svenson, A. | Estimating environmentally important properties of chemicals from the chemical structure | 2003 | 2016/02/08 | |||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 0.209 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Peter C. von der Ohe, Ralph Kühne, Ralf-Uwe Ebert, Rolf Altenburger, Matthias Liess, and Gerrit Schüürmann | Structural Alerts-A New Classification Model to Discriminate Excess Toxicity from Narcotic Effect Levels of Organic Compounds in the Acute Daphnid Assay | 2005 | 2016/02/08 | |||||||
| 甲殻類 | Daphnia magna | mortality and mobility | LC50 | 14 | days | >86 | μg/L | × | 12 ECHA Information on Registered Substances | study report | 2008 | 2016/03/18 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC100 | 48 | hours | 1.3 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 11 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1994 | 2016/03/18 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.38 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.18 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/03/18 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 26 | μg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1994 | 2016/03/18 | ||||||
| 甲殻類 | Daphnia magna | mortality and mobility | LC50 | 48 | hours | >0.2 | × | 12 ECHA Information on Registered Substances | study report | 2008 | 2016/03/18 | ||||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | >0.1 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1999 | 2016/03/27 | ||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 21 | days | 57 | μg/L | ○ | water control, solvent control, 5, 10, 20, 40, 80 µg a.i./L | < LOQ (water and solvent control), 5, 10, 20, 40, 81 µg a.i./L | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Daphnia magna | mortality | NOEC | 21 | days | 40 | μg/L | ○ | water control, solvent control, 5, 10, 20, 40, 80 µg a.i./L | < LOQ (water and solvent control), 5, 10, 20, 40, 81 µg a.i./L | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 70 | μg/L | ○ | water control, solvent control, 5, 10, 20, 40, 80 µg a.i./L | < LOQ (water and solvent control), 5, 10, 20, 40, 81 µg a.i./L | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 40 | μg/L | ○ | water control, solvent control, 5, 10, 20, 40, 80 µg a.i./L | < LOQ (water and solvent control), 5, 10, 20, 40, 81 µg a.i./L | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Daphnia magna | other: growth and sub-lethal effects | NOEC | 21 | days | 20 | μg/L | ○ | water control, solvent control, 5, 10, 20, 40, 80 µg a.i./L | < LOQ (water and solvent control), 5, 10, 20, 40, 81 µg a.i./L | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Daphnia magna | mortality and mobility | LC50 | 14 | days | 86 | μg/L [nominal, act.ingr.] | × | 12 ECHA Information on Registered Substances | study report | 2008 | 2020/03/18 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 21 | days | 8 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., F. Moberts, and G. Niebeek | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. II. Effects on Survival, Reproduction and Growth of Daphnia magna | Aquat. Toxicol.7 | 1988 | |||||||
| 甲殻類 | Crassostrea gigas | NOEL | 48 | hours | <1.3 | ppb | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | ICI Plant Protection Division, England | 1992 | 2019/02/27 | ||||||||
| 甲殻類 | Daphnia magna | LC50 | 21 | days | 0.008 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Moberts F and Niebeek G | Aquatic toxicological aspects of dithiocarbamatrs and related compounds. II. Effects on survival, reproduction and growth of Daphnia magna | Aquatic toxicology | 1985 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | LC50 | 21 | days | 0.008 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Moberts F and Niebeek G | Aquatic toxicological aspects of dithiocarbamatrs and related compounds. II. Effects on survival, reproduction and growth of Daphnia magna | Aquatic toxicology | 1985 | 2018/12/06 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 21 | days | 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 | Van Leeuwen, C.J., F. Moberts, and G. Niebeek | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. II. Effects on Survival, Reproduction and Growth of Daphnia magna. | Aquat.Toxicol. | 1985 | 2016/03/07 | |||||
| 甲殻類 | Daphnia magna | LC50 | 21 | days | 0.008 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Moberts F and Niebeek G | Aquatic toxicological aspects of dithiocarbamatrs and related compounds. II. Effects on survival, reproduction and growth of Daphnia magna | Aquatic toxicology | 1985 | 2016/02/22 | ||||||
| 甲殻類 | Daphnia magna | mobility | NOEC | 24 | hours | 0.027 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2016/02/22 | ||||||
| 甲殻類 | Daphnia magna | LOEC | 24 | hours | 0.045 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2016/02/22 | |||||||
| 甲殻類 | Daphnia magna | mobility | LOEC | 48 | hours | 0.027 | mg/L | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute immobilisation of Bis (dimethylthiocarbamoyl) disulfide in Daphnia magna | 2008 | 2016/02/22 | ||||||
| 甲殻類 | Daphnia magna | EGGHATCH, SURVIVE, GROWTH | LOEC | 21 | days | 40 | ppb | 3 USEPA Pesticide Ecotoxicity Database | E. Arnold | 2015 | 2018/03/07 | ||||||||
| 甲殻類 | Daphnia magna | EGGHATCH, SURVIVE, GROWTH | NOEL | 21 | days | 20 | ppb | 3 USEPA Pesticide Ecotoxicity Database | E. Arnold | 2015 | 2018/03/07 | ||||||||
| 甲殻類 | Daphnia magna | EGGHATCH, SURVIVE, GROWTH | LOEC | 21 | days | 40 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | E. Arnold | 2015 | 2016/02/02 | ||||||||
| 甲殻類 | Daphnia magna | mortality | EC50 | 21 | days | 57 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | ||||||
| 甲殻類 | Daphnia magna | mobility | 48 | hours | 0.14 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | |||||||
| 甲殻類 | Daphnia magna | EGGHATCH, SURVIVE, GROWTH | NOEL | 21 | days | 20 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | E. Arnold | 2015 | 2016/02/02 | ||||||||
| 甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 70 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | ||||||
| 甲殻類 | Daphnia magna | mortality | 21 | days | 40 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | |||||||
| 甲殻類 | Daphnia magna | growth and sub-lethal effects | 21 | days | 20 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | |||||||
| 甲殻類 | Daphnia magna | reproduction | 21 | days | 40 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | NOEC | 42 | days | 0.012 | mg/L | ○ | 15, 25, 39, 63, 100 ug/L of the formulation THIRAM 80 WG (12, 20, 31, 50, 80 ug/L of the active ingredient Thiram) | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 42 | days | 0.02 | mg/L | ○ | 15, 25, 39, 63, 100 ug/L of the formulation THIRAM 80 WG (12, 20, 31, 50, 80 ug/L of the active ingredient Thiram) | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | LOEC | 28 | days | 0.02 | mg/L [nominal, act.ingr.] | ○ | 15, 25, 39, 63, 100 ug/L of the formulation THIRAM 80 WG (12, 20, 31, 50, 80 ug/L of the active ingredient Thiram) | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | 2020/03/18 | |||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentDeformation | LOEL LOEL | 20 | hours | 4 | ppb [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., J.K. La Du, M. Vue, N. Alzarban, and R.L. Tanguay | Dithiocarbamates have a Common Toxic Effect on Zebrafish Body Axis Formation | Toxicol. Appl. Pharmacol.216(1) | 2006 | |||||||
| 魚類 | Danio rerio (Zebrafish) | BehaviorActivity, general | NOEC NOEC | 20 | hours | 0.18～90 | nM [Active ingredient] | 0 nM / 0.18 nM / 0.35 nM / 0.70 nM / 1.41 nM / 2.81 nM / 5.63 nM / 11.25 nM / 22.5 nM / 45 nM / 90 nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Raftery,T.D., G.M. Isales, K.L. Yozzo, and D.C. Volz | High-Content Screening Assay for Identification of Chemicals Impacting Spontaneous Activity in Zebrafish Embryos | Environ. Sci. Technol.48(1) | 2014 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | ReproductionProgeny counts/numbers | NOEC NOEC | 210 | days | 1.1 | ppb [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 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | MortalitySurvival | NOEC NOEC | 210 | days | 1.1 | ppb [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 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GrowthGrowth, general | LOEC LOEC | 60 | days | <=0.32 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3) | 1986 | |||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentDeformation | NOEL NOEL | 20 | hours | <4 | ppb [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., J.K. La Du, M. Vue, N. Alzarban, and R.L. Tanguay | Dithiocarbamates have a Common Toxic Effect on Zebrafish Body Axis Formation | Toxicol. Appl. Pharmacol.216(1) | 2006 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | MortalitySurvival | LOEC LOEC | 210 | days | 2.2 | ppb [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 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | 20 | hours | 0.9～50 | μM [Active ingredient] | 0 uM / 0.09 uM / 0.19 uM / 0.39 uM / 0.78 uM / 1.56 uM / 3.125 uM / 6.25 uM / 12.5 uM / 25 uM / 50 uM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Raftery,T.D., G.M. Isales, K.L. Yozzo, and D.C. Volz | High-Content Screening Assay for Identification of Chemicals Impacting Spontaneous Activity in Zebrafish Embryos | Environ. Sci. Technol.48(1) | 2014 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | 24 | hours | 1000 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3) | 1985 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | ReproductionProgeny counts/numbers | LOEC LOEC | 210 | days | 2.2 | ppb [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 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 60 | days | 1.1 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3) | 1986 | |||||||
| 魚類 | Danio rerio (Zebrafish) | GrowthArea | NOEC NOEC | 20 | hours | 90 | nM [Active ingredient] | 0 nM / 0.18 nM / 0.35 nM / 0.70 nM / 1.41 nM / 2.81 nM / 5.63 nM / 11.25 nM / 22.5 nM / 45 nM / 90 nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Raftery,T.D., G.M. Isales, K.L. Yozzo, and D.C. Volz | High-Content Screening Assay for Identification of Chemicals Impacting Spontaneous Activity in Zebrafish Embryos | Environ. Sci. Technol.48(1) | 2014 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LOEC LOEC | 60 | days | 1 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | GrowthGrowth, general | LOEC LOEC | 60 | days | 0.56 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MultipleMultiple effects reported as one result | LOEC LOEC | 60 | days | <=0.32 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MultipleMultiple effects reported as one result | EC50 EC50 | 60 | days | 0.64 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3) | 1986 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC50 LC50 | 7 | days | 34 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1) | 1990 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC50 LC50 | 116 | hours | 15 | μM [Formulation] | 0 uM / 0.0064 uM / 0.064 uM / 0.64 uM / 6.4 uM / 64 uM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Truong,L., S.M. Bugel, A. Chlebowski, C.Y. Usenko, M.T. Simonich, S.L.M. Simonich, and R.L. Tanguay | Optimizing Multi-Dimensional High Throughput Screening Using Zebrafish | Reprod. Toxicol.10(65) | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC50 LC50 | 20 | hours | 40～400 | ppb [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., J.K. La Du, M. Vue, N. Alzarban, and R.L. Tanguay | Dithiocarbamates have a Common Toxic Effect on Zebrafish Body Axis Formation | Toxicol. Appl. Pharmacol.216(1) | 2006 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC50 LC50 | 116 | hours | 50 | μM [Formulation] | 0 uM / 0.0064 uM / 0.064 uM / 0.64 uM / 6.4 uM / 64 uM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Truong,L., S.M. Bugel, A. Chlebowski, C.Y. Usenko, M.T. Simonich, S.L.M. Simonich, and R.L. Tanguay | Optimizing Multi-Dimensional High Throughput Screening Using Zebrafish | Reprod. Toxicol.10(65) | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LOEC LOEC | 7 | days | 1 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1) | 1990 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC50 LC50 | 20 | hours | 14 | μM [Active ingredient] | 0 uM / 0.09 uM / 0.19 uM / 0.39 uM / 0.78 uM / 1.56 uM / 3.125 uM / 6.25 uM / 12.5 uM / 25 uM / 50 uM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Raftery,T.D., G.M. Isales, K.L. Yozzo, and D.C. Volz | High-Content Screening Assay for Identification of Chemicals Impacting Spontaneous Activity in Zebrafish Embryos | Environ. Sci. Technol.48(1) | 2014 | ||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentTeratogenic measurements | EC50 EC50 | 7 | days | 6 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1) | 1990 | |||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentDeformation | EC50 EC50 | 120 | hours | 50 | nM [Active ingredient] | 0 nM / 0 nM / 100 nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Boxtel,A.L., B. Pieterse, P. Cenijn, J.H. Kamstra, A. Brouwer, W. Van Wieringen, J. De Boer, and J. Legler | Dithiocarbamates Induce Craniofacial Abnormalities and Downregulate sox9a During Zebrafish Development | Toxicol. Sci.117(1) | 2010 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MultipleMultiple effects reported as one result | EC50 EC50/ | 120 | hours | <0.0014 | μM [Formulation] | 0 uM / 0.001 uM / 0.004 uM / 0.012 uM / 0.030 uM / 0.110 uM / 0.320 uM / 1.000 uM / 2.960 uM / 8.800 uM / 26.600 uM / 80.000 uM | 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) | 2012 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MultipleMultiple effects reported as one result | LOEC LOEC | 7 | days | 1 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1) | 1990 | |||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentDeformation | LOEC LOEC | 117 | hours | 7.5 | nM [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Boxtel,A.L., J.H. Kamstra, D.M. Fluitsma, and J. Legler | Dithiocarbamates are Teratogenic to Developing Zebrafish Through Inhibition of Lysyl Oxidase Activity | Toxicol. Appl. Pharmacol.244(2) | 2010 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth (Growth, general) | LOEC | 60 | days | <=0.00032 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 0.13 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LOEC | 60 | days | 0.001 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth (Growth, general) | LOEC | 60 | days | 0.00056 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Multiple (Multiple effects reported as one result) | LOEC | 60 | days | <=0.00032 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Lemna gibba | Population (Abundance) | EC50 | 7 | days | 1.6 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Lemna gibba | Population (Abundance) | EC50 | 7 | days | 1.6 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Lemna gibba | Population (Abundance) | NOEL | 7 | days | <0.057 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 0.064911 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54:1387-1390 | 1997 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 0.062507 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54:1387-1390 | 1997 | 2019/02/13 | ||||||
| 魚類 | others Rasbora heteromorpha | Mortality | LC10 | 2 | days | 0.0065 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tooby,T.E., P.A. Hursey, and J.S. Alabaster | The Acute Toxicity of 102 Pesticides and Miscellaneous Substances to Fish | Chem. Ind. (Lond.)21:523-526 | 1975 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | 0.3 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, and H.C.M. Overbeek | Sublethal Effects of Tetramethylthiuram Disulfide (Thiram) in Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(1): 13-19 | 1986 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tubifex tubifex | Mortality | LC50 | 2 | days | 0.67 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Voronkin,A.S., and Y.T. Loshakov | Toxic Effect of Pesticides on Tubifex tubifex | Exp. Water Toxicol. (Eksp. Vodn. Toksikol. )5:169-178 | 1973 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Dugesia gonocephala | Mortality | LC50 | 1 | days | 0.53 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Dugesia gonocephala | Mortality | LC50 | 2 | days | 0.26 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Dugesia gonocephala | Mortality | LC50 | 4 | days | 0.048 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Development (Deformation) | EC50 | 5 | days | 0.01202 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Boxtel,A.L., B. Pieterse, P. Cenijn, J.H. Kamstra, A. Brouwer, W. Van Wieringen, J. De Boer, and J. Legler | Dithiocarbamates Induce Craniofacial Abnormalities and Downregulate sox9a During Zebrafish Development | Toxicol. Sci.117(1): 209-217 | 2010 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Dugesia gonocephala | Mortality | LC50 | 3 | days | 0.088 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) | Intoxication (Immobile) | NOEL | 2 | days | <0.0013 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) | Intoxication (Immobile) | EC50 | 2 | days | 0.0047 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Unio tumidus | Mortality | 3 | days | 0.1 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Doyotte,A., C. Cossu, M.C. Jacquin, M. Babut, and P. Vasseur | Antioxidant Enzymes, Glutathione and Lipid Peroxidation as Relevant Biomarkers of Experimental or Field Exposure in the Gills and the Digestive Gland of the Freshwater Bivalve Unio tumidus | Aquat. Toxicol.39:93-110 | 1997 | 2019/02/13 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 60 | days | 0.0011 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 0.83 | days | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., J.K. La Du, M. Vue, N. Alzarban, and R.L. Tanguay | Dithiocarbamates have a Common Toxic Effect on Zebrafish Body Axis Formation | Toxicol. Appl. Pharmacol.216(1): 55-68 | 2006 | 2019/02/13 | |||||||
| 魚類 | Poecilia reticulata (Guppy) Brachionus plicatilis | Mortality | LC50 | 1 | days | 0.05 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kyriakopoulou,K., P. Anastasiadou, and K. Machera | Comparative Toxicities of Fungicide and Herbicide Formulations on Freshwater and Marine Species | Bull. Environ. Contam. Toxicol.82(3): 290-295 | 2009 | 2019/02/13 | ||||||
| 魚類 | others Ictalurus punctatus | Mortality | LC50 | 0.16 | days | >1 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clemens,H.P., and K.E. Sneed | Lethal Doses of Several Commercial Chemicals for Fingerling Channel Catfish | U.S.Fish.Wildl.Serv., Spec.Sci.Rep.- Fish No.316, Washington, DC:10 p. | 1959 | 2019/02/13 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 0.042 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Development (Teratogenic measurements) | EC50 | 7 | days | 0.006 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1): 42-52 | 1990 | 2019/02/13 | ||||||
| 魚類 | others Tilapia rendalli | Genetics (Micronuclei) | NOEL | 4 | days | 2.5 | その他others [mg/kg bdwt, Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Grisolia,C.K. | A Comparison Between Mouse and Fish Micronucleus Test Using Cyclophosphamide, Mitomycin C and Various Pesticides | Mutat. Res.518(2): 145-150 | 2002 | 2019/02/13 | ||||||
| 魚類 | others Tilapia rendalli | Genetics (Micronuclei) | LOEL | 4 | days | 5 | その他others [mg/kg bdwt, Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Grisolia,C.K. | A Comparison Between Mouse and Fish Micronucleus Test Using Cyclophosphamide, Mitomycin C and Various Pesticides | Mutat. Res.518(2): 145-150 | 2002 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) | Mortality | LC50 | 4 | days | 0.27 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3): 145-164 | 1985 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 7 | days | 0.034 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1): 42-52 | 1990 | 2019/02/13 | ||||||
| 魚類 | others Ictalurus punctatus | Mortality | LC50 | 0.08 | days | >1 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clemens,H.P., and K.E. Sneed | Lethal Doses of Several Commercial Chemicals for Fingerling Channel Catfish | U.S.Fish.Wildl.Serv., Spec.Sci.Rep.- Fish No.316, Washington, DC:10 p. | 1959 | 2019/02/13 | ||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | Mortality | LC50 | 4 | days | 0.54 | mg/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 | 2019/02/13 | ||||||
| 魚類 | others Rasbora heteromorpha | Mortality | LC50 | 4 | days | 0.007 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tooby,T.E., P.A. Hursey, and J.S. Alabaster | The Acute Toxicity of 102 Pesticides and Miscellaneous Substances to Fish | Chem. Ind. (Lond.)21:523-526 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Rasbora heteromorpha | Mortality | LC10 | 1 | days | 0.008 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tooby,T.E., P.A. Hursey, and J.S. Alabaster | The Acute Toxicity of 102 Pesticides and Miscellaneous Substances to Fish | Chem. Ind. (Lond.)21:523-526 | 1975 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Lemna gibba | Population (Abundance) | NOEL | 7 | days | <0.057 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Multiple (Multiple effects reported as one result) | EC50 | 5 | days | <0.000336 | mg/L [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 | 2019/02/13 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 0.035581 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54:1387-1390 | 1997 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Spirostomum ambiguum | Morphology (Abnormal) | EC50 | 1 | days | 0.006 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nalecz-Jawecki,G., E. Kucharczyk, and J. Sawicki | The Sensitivity of Protozoan Spirostomum ambiguum to Selected Pesticides | Fresenius Environ. Bull.11(2): 98-101 | 2002 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Paramecium caudatum | Population (Abundance) | IC50 | 2 | days | 0.324559 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Miyoshi,N., T. Kawano, M. Tanaka, T. Kadono, T. Kosaka, M. Kunimoto, T. Takahashi, and H. Hosoya | Use of Paramecium Species in Bioassays for Environmental Risk Management: Determination of IC50 Values for Water Pollutants | J. Health Sci.49(6): 429-435 | 2003 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena pyriformis | Enzyme(s) (Non-specific esterases) | IC50 | 0.04 | days | 0.025 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bogaerts,P., J. Bohatier, and F. Bonnemoy | Use of the Ciliated Protozoan Tetrahymena pyriformis for the Assessment of Toxicity and Quantitative Structure-Activity Relationships of Xenobiotics: Comparison with the Microtox Test | Ecotoxicol. Environ. Saf.49(3): 293-301 | 2001 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Paramecium trichium | Population (Abundance) | IC50 | 5 | days | 0.264456 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Miyoshi,N., T. Kawano, M. Tanaka, T. Kadono, T. Kosaka, M. Kunimoto, T. Takahashi, and H. Hosoya | Use of Paramecium Species in Bioassays for Environmental Risk Management: Determination of IC50 Values for Water Pollutants | J. Health Sci.49(6): 429-435 | 2003 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena pyriformis | Population (Population growth rate) | IC50 | 0.37 | days | 0.125 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bogaerts,P., J. Bohatier, and F. Bonnemoy | Use of the Ciliated Protozoan Tetrahymena pyriformis for the Assessment of Toxicity and Quantitative Structure-Activity Relationships of Xenobiotics: Comparison with the Microtox Test | Ecotoxicol. Environ. Saf.49(3): 293-301 | 2001 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Paramecium trichium | Population (Abundance) | IC50 | 2 | days | 0.048082 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Miyoshi,N., T. Kawano, M. Tanaka, T. Kadono, T. Kosaka, M. Kunimoto, T. Takahashi, and H. Hosoya | Use of Paramecium Species in Bioassays for Environmental Risk Management: Determination of IC50 Values for Water Pollutants | J. Health Sci.49(6): 429-435 | 2003 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Paramecium caudatum | Population (Abundance) | IC50 | 5 | days | 0.589016 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Miyoshi,N., T. Kawano, M. Tanaka, T. Kadono, T. Kosaka, M. Kunimoto, T. Takahashi, and H. Hosoya | Use of Paramecium Species in Bioassays for Environmental Risk Management: Determination of IC50 Values for Water Pollutants | J. Health Sci.49(6): 429-435 | 2003 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Spirostomum ambiguum | Mortality | LC50 | 1 | days | 0.015 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Nalecz-Jawecki,G., E. Kucharczyk, and J. Sawicki | The Sensitivity of Protozoan Spirostomum ambiguum to Selected Pesticides | Fresenius Environ. Bull.11(2): 98-101 | 2002 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Spirostomum teres | Mortality | LC50 | 1 | days | 0.433 | mg/L [Total] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Twagilimana,L., J. Bohatier, CA Groliere, F. Bonnemoy, and D. Sargos | A New Low-Cost Microbiotest with the Protozoan Spirostomum teres: Culture Conditions and Assessment of Sensitivity of the Ciliate to 14 Pure Chemicals | Ecotoxicol. Environ. Saf.41(3): 231-244 | 1998 | 2019/02/13 | ||||||
| 魚類 | others Rasbora heteromorpha | Mortality | LC50 | 2 | days | 0.012 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tooby,T.E., P.A. Hursey, and J.S. Alabaster | The Acute Toxicity of 102 Pesticides and Miscellaneous Substances to Fish | Chem. Ind. (Lond.)21:523-526 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Rasbora heteromorpha | Mortality | LC50 | 1 | days | 0.02 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tooby,T.E., P.A. Hursey, and J.S. Alabaster | The Acute Toxicity of 102 Pesticides and Miscellaneous Substances to Fish | Chem. Ind. (Lond.)21:523-526 | 1975 | 2019/02/13 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality (Survival) | LOEC | 210 | days | 0.0022 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 0.28 | mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2019/02/13 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 0.28 | mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2019/02/13 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 0.013198 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54:1387-1390 | 1997 | 2019/02/13 | ||||||
| 魚類 | others Ictalurus punctatus | Mortality | LC50 | 1 | days | >1 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clemens,H.P., and K.E. Sneed | Lethal Doses of Several Commercial Chemicals for Fingerling Channel Catfish | U.S.Fish.Wildl.Serv., Spec.Sci.Rep.- Fish No.316, Washington, DC:10 p. | 1959 | 2019/02/13 | ||||||
| 魚類 | others Ictalurus punctatus | Mortality | LC50 | 3 | days | 0.79 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clemens,H.P., and K.E. Sneed | Lethal Doses of Several Commercial Chemicals for Fingerling Channel Catfish | U.S.Fish.Wildl.Serv., Spec.Sci.Rep.- Fish No.316, Washington, DC:10 p. | 1959 | 2019/02/13 | ||||||
| 魚類 | others Ictalurus punctatus | Mortality | LC50 | 0.04 | days | >1 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clemens,H.P., and K.E. Sneed | Lethal Doses of Several Commercial Chemicals for Fingerling Channel Catfish | U.S.Fish.Wildl.Serv., Spec.Sci.Rep.- Fish No.316, Washington, DC:10 p. | 1959 | 2019/02/13 | ||||||
| 魚類 | others Ictalurus punctatus | Mortality | LC50 | 0.33 | days | >1 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clemens,H.P., and K.E. Sneed | Lethal Doses of Several Commercial Chemicals for Fingerling Channel Catfish | U.S.Fish.Wildl.Serv., Spec.Sci.Rep.- Fish No.316, Washington, DC:10 p. | 1959 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 0.83 | days | 3.365805 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Raftery,T.D., G.M. Isales, K.L. Yozzo, and D.C. Volz | High-Content Screening Assay for Identification of Chemicals Impacting Spontaneous Activity in Zebrafish Embryos | Environ. Sci. Technol.48(1): 804-810 | 2014 | 2019/02/13 | ||||||
| 魚類 | others Ictalurus punctatus | Mortality | LC50 | 2 | days | >0.63 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clemens,H.P., and K.E. Sneed | Lethal Doses of Several Commercial Chemicals for Fingerling Channel Catfish | U.S.Fish.Wildl.Serv., Spec.Sci.Rep.- Fish No.316, Washington, DC:10 p. | 1959 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Cloeon dipterum | Mortality | LC50 | 2 | days | 0.8 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, in Larvae of the Mayfly, Cloeon dipterum - Effects of Various Parameters | Hydrobiologia101(3): 215-221 | 1983 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | LOEC | 7 | days | 0.001 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1): 42-52 | 1990 | 2019/02/13 | ||||||
| 魚類 | others Ictalurus punctatus | Mortality | LC50 | 4 | days | 0.79 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Clemens,H.P., and K.E. Sneed | Lethal Doses of Several Commercial Chemicals for Fingerling Channel Catfish | U.S.Fish.Wildl.Serv., Spec.Sci.Rep.- Fish No.316, Washington, DC:10 p. | 1959 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Multiple (Multiple effects reported as one result) | LOEC | 7 | days | 0.001 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1): 42-52 | 1990 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Development (Deformation) | LOEL | 0.83 | days | 0.004 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., J.K. La Du, M. Vue, N. Alzarban, and R.L. Tanguay | Dithiocarbamates have a Common Toxic Effect on Zebrafish Body Axis Formation | Toxicol. Appl. Pharmacol.216(1): 55-68 | 2006 | 2019/02/13 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality (Survival) | NOEC | 210 | days | 0.0011 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction (Progeny counts/numbers) | NOEC | 210 | days | 0.0011 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Cloeon dipterum | Mortality | LC50 | 1 | days | 1.03 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, in Larvae of the Mayfly, Cloeon dipterum - Effects of Various Parameters | Hydrobiologia101(3): 215-221 | 1983 | 2019/02/13 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 48 | hours | 0.190968 | その他others [mol/L] | 17 Aquatic OASIS (OECD QSAR Toolbox) | Unnamed | Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan | Chemicals Investigation and Testing Institute. 1992. Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan, ISBN 4-98074-101-1. Japan Chemical Industry Ecology-Toxicology&Information Center; | 1992 | 2019/02/22 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | NOEL | 4 | days | 0.1 | mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Growth (Area) | NOEC | 0.83 | days | 0.021637 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Raftery,T.D., G.M. Isales, K.L. Yozzo, and D.C. Volz | High-Content Screening Assay for Identification of Chemicals Impacting Spontaneous Activity in Zebrafish Embryos | Environ. Sci. Technol.48(1): 804-810 | 2014 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Behavior (Activity, general) | NOEC | 0.83 | days | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Raftery,T.D., G.M. Isales, K.L. Yozzo, and D.C. Volz | High-Content Screening Assay for Identification of Chemicals Impacting Spontaneous Activity in Zebrafish Embryos | Environ. Sci. Technol.48(1): 804-810 | 2014 | 2019/02/13 | |||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | Mortality | NOEL | 4 | days | 0.09 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction (Progeny counts/numbers) | LOEC | 210 | days | 0.0022 | mg/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 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Development (Deformation) | NOEL | 0.83 | days | <0.004 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., J.K. La Du, M. Vue, N. Alzarban, and R.L. Tanguay | Dithiocarbamates have a Common Toxic Effect on Zebrafish Body Axis Formation | Toxicol. Appl. Pharmacol.216(1): 55-68 | 2006 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Cloeon dipterum | Mortality | LC50 | 2 | days | 1.3 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, in Larvae of the Mayfly, Cloeon dipterum - Effects of Various Parameters | Hydrobiologia101(3): 215-221 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Cloeon dipterum | Mortality | LC50 | 4 | days | 1.01 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, in Larvae of the Mayfly, Cloeon dipterum - Effects of Various Parameters | Hydrobiologia101(3): 215-221 | 1983 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 0.048 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kikuchi,M., T. Miyagaki, and M. Wakabayashi | Evaluation of Pesticides Used in Golf Links by Acute Toxicity Test on Rainbow Trout | Nippon Suisan Gakkaishi62(3): 414-419 | 1996 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | 0.26 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, and H.C.M. Overbeek | Sublethal Effects of Tetramethylthiuram Disulfide (Thiram) in Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(1): 13-19 | 1986 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Cloeon dipterum | Mortality | LC50 | 3 | days | 1.08 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, in Larvae of the Mayfly, Cloeon dipterum - Effects of Various Parameters | Hydrobiologia101(3): 215-221 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Cloeon dipterum | Mortality | LC50 | 3 | days | 0.56 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, in Larvae of the Mayfly, Cloeon dipterum - Effects of Various Parameters | Hydrobiologia101(3): 215-221 | 1983 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Multiple (Multiple effects reported as one result) | EC50 | 60 | days | 0.00064 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2019/02/13 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | 1 | days | 1 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3): 327-338 | 1985 | 2019/02/13 | |||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | 0.83 | days | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Raftery,T.D., G.M. Isales, K.L. Yozzo, and D.C. Volz | High-Content Screening Assay for Identification of Chemicals Impacting Spontaneous Activity in Zebrafish Embryos | Environ. Sci. Technol.48(1): 804-810 | 2014 | 2019/02/13 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 0.4 | mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C.: | 1992 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | LC50 | 3 | days | 0.021 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | LC50 | 1 | days | 0.017 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | LC50 | 2 | days | 0.014 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | LC50 | 1 | days | 0.025 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | LC50 | 4 | days | 0.013 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | LC50 | 2 | days | 0.022 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Cloeon dipterum | Mortality | LC50 | 1 | days | 1.92 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, in Larvae of the Mayfly, Cloeon dipterum - Effects of Various Parameters | Hydrobiologia101(3): 215-221 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | LC50 | 4 | days | 0.021 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Mortality | LC50 | 3 | days | 0.013 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., D. Marchal-Segault, and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, on Several Animals Species of Freshwater (Toxicite Aigue d'un Fongicide Dithiocarbamate, le Thirame, vis-a-vis de Plusieurs Especes Animales d'eau Douce) | Environ. Pollut. A.31(3): 177-189 | 1983 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Cloeon dipterum | Mortality | LC50 | 4 | days | 0.39 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Seuge,J., and R. Bluzat | Acute Toxicity of a Dithiocarbamate Fungicide, Thiram, in Larvae of the Mayfly, Cloeon dipterum - Effects of Various Parameters | Hydrobiologia101(3): 215-221 | 1983 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 400 | 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 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | 1 | days | 1000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3): 327-338 | 1985 | 2016/03/25 | |||||||
| 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 | Danio rerio (Zebrafish) | Mortality | 1 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3): 327-338 | 1985 | 2016/03/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | 1 | days | 1000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Jouany,J.M., R. Truhaut, P. Vasseur, D. Klein, J.F. Ferard, and P. Deschamps | An Example of Interaction between Environmental Pollutants: Modification of Thiram Toxicity to Freshwater Organisms by Nitrites or Nitrates in Relation to Nitrosamine Synthesis | Ecotoxicol. Environ. Saf.9(3): 327-338 | 1985 | 2016/03/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Behavior | 2.88 | days | 93 | その他others [mg/kg bdwt] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Loeb,H.A., and W.H. Kelly | Acute Oral Toxicity of 1,496 Chemicals Force-Fed to Carp | U.S.Fish.Wildl.Serv., Sp.Sci.Rep.-Fish.No.471, Washington, D.C.:124 p. | 1963 | 2016/03/25 | |||||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | 2.88 | days | 121 | その他others [mg/kg bdwt] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Loeb,H.A., and W.H. Kelly | Acute Oral Toxicity of 1,496 Chemicals Force-Fed to Carp | U.S.Fish.Wildl.Serv., Sp.Sci.Rep.-Fish.No.471, Washington, D.C.:124 p. | 1963 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | No Group Code | EC50 | 60 | days | 0.64 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 0.26 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54:1387-1390 | 1997 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 0.27 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54:1387-1390 | 1997 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Cellular Effects | 21 | days | 5 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., T. Helder, and W. Seinen | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. IV. Teratogenicity and Histopathology in Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 147-159 | 1986 | 2016/03/25 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 48 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kikuchi,M., T. Miyagaki, and M. Wakabayashi | Evaluation of Pesticides Used in Golf Links by Acute Toxicity Test on Rainbow Trout | Nippon Suisan Gakkaishi62(3): 414-419 | 1996 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 60 | days | 1.1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 280 | 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 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 130 | 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 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | 260 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, and H.C.M. Overbeek | Sublethal Effects of Tetramethylthiuram Disulfide (Thiram) in Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(1): 13-19 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 1 | days | 300 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, and H.C.M. Overbeek | Sublethal Effects of Tetramethylthiuram Disulfide (Thiram) in Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(1): 13-19 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | LOEC | 60 | days | <=0.32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LOEC | 60 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | LOEC | 60 | days | 0.56 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | No Group Code | LOEC | 60 | days | <=0.32 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., A. Espeldoorn, and F. Mol | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(2/3): 129-145 | 1986 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | NOEL | 4 | days | 100 | 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 | 2016/03/25 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Physiology | 1 | days | 180 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, and H.C.M. Overbeek | Sublethal Effects of Tetramethylthiuram Disulfide (Thiram) in Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(1): 13-19 | 1986 | 2016/03/25 | |||||||
| 魚類 | Danio rerio (Zebrafish) | No Group Code | EC50 | 5 | days | <0.0014 | 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 | Danio rerio (Zebrafish) | Mortality | LC50 | 7 | days | 34 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1): 42-52 | 1990 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Growth | EC50 | 7 | days | 6 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1): 42-52 | 1990 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Growth | NOEL | 20 | hours | <4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., J.K. La Du, M. Vue, N. Alzarban, and R.L. Tanguay | Dithiocarbamates have a Common Toxic Effect on Zebrafish Body Axis Formation | Toxicol. Appl. Pharmacol.216(1): 55-68 | 2006 | 2016/03/25 | ||||||
| 魚類 | Poecilia reticulata (Guppy) | Mortality | LC50 | 4 | days | 270 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3): 145-164 | 1985 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 20 | hours | 40～400 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., J.K. La Du, M. Vue, N. Alzarban, and R.L. Tanguay | Dithiocarbamates have a Common Toxic Effect on Zebrafish Body Axis Formation | Toxicol. Appl. Pharmacol.216(1): 55-68 | 2006 | 2016/03/25 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 280 | 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 | 2016/03/25 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 42 | 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 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 148 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54:1387-1390 | 1997 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | No Group Code | LOEC | 7 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1): 42-52 | 1990 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction | LOEC | 210 | days | 2.2 | 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 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Mortality | LOEC | 7 | days | 1 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicol. Environ. Saf.20(1): 42-52 | 1990 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LOEC | 210 | days | 2.2 | 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 | 2016/03/25 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Growth | LOEL | 20 | hours | 4 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tilton,F., J.K. La Du, M. Vue, N. Alzarban, and R.L. Tanguay | Dithiocarbamates have a Common Toxic Effect on Zebrafish Body Axis Formation | Toxicol. Appl. Pharmacol.216(1): 55-68 | 2006 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | NOEC | 210 | days | 1.1 | 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 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Reproduction | NOEC | 210 | days | 1.1 | 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 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 54.9 | nM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54:1387-1390 | 1997 | 2016/03/25 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | NOEC | 96 | hours | 0.1 | mg/L | ○ | 0.10, 0.18, 0.32, 0.56, 1.0 mg/L | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 0.046 | mg/L | ○ | 0 (blank), 0.0032, 0.010, 0.032, 0.10, 0.32 and 1.0 mg a.i./L | blank, below the limit of detection, below the limit of detection, below the limit of detection, 0.00519, 0.0788, 0.722 mg/L | 12 ECHA Information on Registered Substances | 1 | study report | 2000 | |||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 0.13 | mg/L | ○ | 0.056, 0.10, 0.18, 0.32, 0.56 mg a.i./L | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 0.27 | mg/L | ○ | 0.10, 0.18, 0.32, 0.56, 1.0 mg/L | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | ||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | mortality | LC50 | 96 | hours | 0.54 | mg/L | ○ | 0.056, 0.10, 0.18, 0.32, 0.56, 1.0 mg a.i./L | 90- 96% from nominal values, except from the 0.056 mg/L concentration The mean measured values for this test concentration were not obtained at 72 and 96 hours, since levels were below the analytical limit of detection for both those days. | 12 ECHA Information on Registered Substances | 1 | study report | 1992 | |||||
| 魚類 | Mortality | LC50 | 48 | hours | 0.000794 | mmol/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan | Chemicals Investigation and Testing Institute. 1992. Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan, ISBN 4-98074-101-1. Japan Chemical Industry Ecology-Toxicology&Information Center; | 1992 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 96 | hours | 0.01 | mg/L | ○ | 0 (blank), 0.0032, 0.010, 0.032, 0.10, 0.32 and 1.0 mg a.i./L | blank, below the limit of detection, below the limit of detection, below the limit of detection, 0.00519, 0.0788, 0.722 mg/L | 12 ECHA Information on Registered Substances | 1 | study report | 2000 | |||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | NOEC | 96 | hours | <0.056 | ○ | 0.056, 0.10, 0.18, 0.32, 0.56 mg a.i./L | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | |||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | mortality | NOEC | 96 | hours | 0.09 | mg/L [meas. (arithm.mean) act.ingr.] | ○ | 0.056, 0.10, 0.18, 0.32, 0.56, 1.0 mg a.i./L | 90- 96% from nominal values, except from the 0.056 mg/L concentration The mean measured values for this test concentration were not obtained at 72 and 96 hours, since levels were below the analytical limit of detection for both those days. | 12 ECHA Information on Registered Substances | 1 | study report | 1992 | 2020/03/18 | ||||
| 魚類 | Lepomis macrochirus (Bluegill) | MortalityMortality | NOEL NOEL | 96 | hours | 0.1 | ppm [Not coded] | 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 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 24 | hours | 300 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, and H.C.M. Overbeek | Sublethal Effects of Tetramethylthiuram Disulfide (Thiram) in Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(1) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 130 | ppb [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 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 24 | hours | 260 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, and H.C.M. Overbeek | Sublethal Effects of Tetramethylthiuram Disulfide (Thiram) in Rainbow Trout (Salmo gairdneri) | Aquat. Toxicol.9(1) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 48 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kikuchi,M., T. Miyagaki, and M. Wakabayashi | Evaluation of Pesticides Used in Golf Links by Acute Toxicity Test on Rainbow Trout | Nippon Suisan Gakkaishi62(3) | 1996 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 0.26 | μM [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54 | 1997 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | MortalityMortality | LC50 LC50 | 96 | hours | 54.9 | nM [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54 | 1997 | |||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | MortalityMortality | NOEL NOEL | 96 | hours | 0.09 | ppm [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 | |||||||
| 魚類 | Poecilia reticulata (Guppy) | MortalityMortality | LC50 LC50 | 96 | hours | 270 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Leeuwen,C.J., J.L. Maas-Diepeveen, G. Niebeek, W.H.A. Vergouw, P.S. Griffioen, and M.W. Luijken | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. I. Short-Term Toxicity Tests | Aquat. Toxicol.7(3) | 1985 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | MortalityMortality | LC50 LC50 | 96 | hours | 0.28 | ppm [Not coded] | 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 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | MortalityMortality | LC50 LC50 | 96 | hours | 148 | nM [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54 | 1997 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | MortalityMortality | LC50 LC50 | 96 | hours | 42 | ppb [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 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | MortalityMortality | LC50 LC50 | 96 | hours | 280 | ppb [Not coded] | 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 | |||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | MortalityMortality | LC50 LC50 | 96 | hours | 0.54 | ppm [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 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 48 | hours | 400 | ppb [Not coded] | 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 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 0.27 | μM [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Greene,M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas) | Can. J. Fish. Aquat. Sci.54 | 1997 | |||||||
| 魚類 | Cyprinus carpio (Carp) | LC50 | 96 | hours | 100 | μg/L | 2 日本環境省 農薬登録保留基準（水産動植物） | 2018/12/18 | |||||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | NOEC | 96 | hours | 0.076 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2018/12/05 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | breakdown products | LC50 | 24 | hours | 0.26 | mg/L | 10 EHC (Environmental Health Criteria) | VAN LEEUWEN, C.J. | Ecotoxicological aspects of dithiocarbamates | Utrecht, University of Utrecht (Thesis). | 1986 | 2018/12/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) | breakdown products | LC50 | 96 | hours | 0.27 | mg/L | 10 EHC (Environmental Health Criteria) | VAN LEEUWEN, C.J. | Ecotoxicological aspects of dithiocarbamates | Utrecht, University of Utrecht (Thesis). | 1986 | 2018/12/13 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | 0.17 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2018/12/05 | |||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | LOEC | 96 | hours | 0.2 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2018/12/05 | |||||
| 魚類 | Poecilia reticulata (Guppy) | LC50 | 96 | hours | 0.27 | mg/L | 4 OECD SIDS (HPVC) | 3 | Van Leeuwen CJ, Maas-Diepeveen JL, Niebeek G, Vergouwm WHA, Griffioen PS and Luijken MW | Aquatic toxicological aspects of dithiocarbamates and related compounds. I. Short-term toxicity test | Aquatic toxicology | 1985 | 2018/12/05 | ||||||
| 魚類 | Poecilia reticulata (Guppy) | LC50 | 96 | hours | 0.27 | mg/L | 4 OECD SIDS (HPVC) | 3 | Van Leeuwen CJ, Maas-Diepeveen JL, Niebeek G, Vergouwm WHA, Griffioen PS and Luijken MW | Aquatic toxicological aspects of dithiocarbamates and related compounds. I. Short-term toxicity test | Aquatic toxicology | 1985 | 2018/12/05 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | LOEC | 96 | hours | 0.2 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2018/12/05 | |||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | NOEC | 96 | hours | 0.076 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2018/12/05 | |||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | 0.17 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2018/12/05 | |||||
| 魚類 | Cyprinus carpio (Carp) | Mortality | TL50 | 4 | days | 0.3 | 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 | Verma, S.R., I.P. Tonk, and R.C. Dalela | Determination of the Maximum Acceptable Toxicant Concentration (MATC) and the Safe Concentration for Certain Aquatic Pollutants. | Acta Hydrochim.Hydrobiol. | 1981 | 2016/03/07 | |||||
| 魚類 | Cyprinus carpio (Carp) | LC50 | 4 | mg/L | 10 EHC (Environmental Health Criteria) | WORTHING, C.R. & WALKER, S.B. | The pesticide manual: a world compendium, 7th ed. | Croydon, British Crop Protection Council. | 2016/03/06 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 0.13 | mg/L | 10 EHC (Environmental Health Criteria) | WORTHING, C.R. & WALKER, S.B. | The pesticide manual: a world compendium, 7th ed. | Croydon, British Crop Protection Council. | 2016/03/06 | ||||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 0.23 | mg/L | 10 EHC (Environmental Health Criteria) | WORTHING, C.R. & WALKER, S.B. | The pesticide manual: a world compendium, 7th ed. | Croydon, British Crop Protection Council. | 2016/03/06 | ||||||||||
| 魚類 | Poecilia reticulata (Guppy) | LC50 | 96 | hours | 0.27 | mg/L | 10 EHC (Environmental Health Criteria) | VAN LEEUWEN, C.J. | Ecotoxicological aspects of dithiocarbamates | Utrecht, University of Utrecht (Thesis) | 2016/03/06 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 24 | hours | 0.26 | mg/L | 10 EHC (Environmental Health Criteria) | VAN LEEUWEN, C.J. | Ecotoxicological aspects of dithiocarbamates | Utrecht, University of Utrecht (Thesis) | 2016/03/06 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 13.2 | 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 | Greene, M.W., and R.M. Kocan | Toxicological Mechanisms of a Multicomponent Agricultural Seed Protectant in the Rainbow Trout (Oncorhynchus mykiss) and Fathead Minnow (Pimephales promelas). | Can.J.Fish.Aquat.Sci. | 1997 | 2016/03/07 | |||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 0.17 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2016/02/22 | ||||||
| 魚類 | Cyprinus carpio (Carp) | 死亡 | LC50 | 96 | hours | 100 | μg/L | 2 日本環境省 農薬登録保留基準（水産動植物） | 環境省 | 水産動植物の被害防止に係る農薬登録保留基準の設定に関する資料 | 2016/02/17 | ||||||||
| 魚類 | Poecilia reticulata (Guppy) | LC50 | 96 | hours | 0.27 | mg/L | 4 OECD SIDS (HPVC) | 3 | Van Leeuwen CJ, Maas-Diepeveen JL, Niebeek G, Vergouwm WHA, Griffioen PS and Luijken MW | Aquatic toxicological aspects of dithiocarbamates and related compounds. I. Short-term toxicity test | Aquatic toxicology | 1985 | 2016/02/22 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 48 | hours | 0.29 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2016/02/22 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 72 | hours | 0.23 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2016/02/22 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | 0.13 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | Unnamed | 1983 | 2019/02/20 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 46 | ppb | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2018/03/07 | |||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 280 | ppb | 3 USEPA Pesticide Ecotoxicity Database | McCann/Bascietto | 1972 | 2018/03/07 | |||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 560 | ppb | 3 USEPA Pesticide Ecotoxicity Database | R. Felthousen | 1979 | 2018/03/07 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 380 | ppb | 3 USEPA Pesticide Ecotoxicity Database | R. Felthousen | 1979 | 2018/03/07 | |||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 48 | hours | 0.191 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | - | Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan | 1992 | 2016/02/08 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 560 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | R. Felthousen | 1979 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 46 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2016/02/02 | |||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 42 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | J.J. Bascietto | 1983 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 126 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | J.J. Bascietto | 1983 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 48 | hours | 400 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | J.McCann/Bascietto | 1983 | 2016/02/02 | |||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 280 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | McCann/Bascietto | 1972 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 380 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | R. Felthousen | 1979 | 2016/02/02 | |||||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | mortality | LC50 | 96 | hours | 0.54 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1992 | 2016/03/18 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | LC50 | 96 | hours | <0.13 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2016/03/18 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | SURVIVE, GROWTH | LC50 | 28 | days | 49.1 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2016/02/02 | ||||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | LC50 | 96 | hours | 540 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | 1993 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 0.046 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2000 | 2016/03/18 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 0.27 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2016/03/18 | ||||||
| 魚類 | Pimephales promelas (Fathead minnow) | number hatched | NOEC | 33 | days | 9.3 | μg/L | ○ | Control, solvent control (dimethyl formamide, DMF), 0.56, 1.1, 2.3, 4.5, 9.0 µg a.i./L | 100 – 104% of nominal concentrations | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 魚類 | Pimephales promelas (Fathead minnow) | other: mortality and growth | LOEC | 33 | days | 9.3 | μg/L | ○ | Control, solvent control (dimethyl formamide, DMF), 0.56, 1.1, 2.3, 4.5, 9.0 µg a.i./L | 100 – 104% of nominal concentrations | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 魚類 | Pimephales promelas (Fathead minnow) | other: mortality and growth | NOEC | 33 | days | 4.6 | μg/L | ○ | Control, solvent control (dimethyl formamide, DMF), 0.56, 1.1, 2.3, 4.5, 9.0 µg a.i./L | 100 – 104% of nominal concentrations | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 60 | days | 0.0011 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van leeuwen CJ, Espeldoorn A and Mol F | Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo Gairdneri) | Aquatic Toxicology | 1986 | 2018/12/05 | ||||||
| 魚類 | Brachydanio rerio (Zebrafish) | LC50 | 7 | days | 0.034 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Grootelaar EMM, and Niebeek G | Fish Embryos as Teratogenicity Screens : A Comparison of Embryotoxicity between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2018/12/05 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | EC50 | 60 | days | 0.00064 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van leeuwen CJ, Espeldoorn A and Mol F | Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo Gairdneri) | Aquatic Toxicology | 1986 | 2018/12/05 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LOEC | 60 | days | 0.001 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van leeuwen CJ, Espeldoorn A and Mol F | Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo Gairdneri) | Aquatic Toxicology | 1986 | 2018/12/05 | |||||
| 魚類 | Brachydanio rerio (Zebrafish) | mortality | LOEC | 7 | days | 0.001 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Grootelaar EMM, and Niebeek G | Fish Embryos as Teratogenicity Screens : A Comparison of Embryotoxicity between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2018/12/05 | |||||
| 魚類 | Brachydanio rerio (Zebrafish) | EC50 | 7 | days | 0.006 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Grootelaar EMM, and Niebeek G | Fish Embryos as Teratogenicity Screens : A Comparison of Embryotoxicity between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2018/12/05 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | EC50 | 60 | days | 0.00064 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van leeuwen CJ, Espeldoorn A and Mol F | Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo Gairdneri) | Aquatic Toxicology | 1986 | 2018/12/05 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 60 | days | 0.0011 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van leeuwen CJ, Espeldoorn A and Mol F | Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo Gairdneri) | Aquatic Toxicology | 1986 | 2018/12/05 | ||||||
| 魚類 | Brachydanio rerio (Zebrafish) | EC50 | 7 | days | 0.006 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Grootelaar EMM, and Niebeek G | Fish Embryos as Teratogenicity Screens : A Comparison of Embryotoxicity between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2018/12/05 | ||||||
| 魚類 | Brachydanio rerio (Zebrafish) | mortality | LOEC | 7 | days | 0.001 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Grootelaar EMM, and Niebeek G | Fish Embryos as Teratogenicity Screens : A Comparison of Embryotoxicity between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2018/12/05 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LOEC | 60 | days | 0.001 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van leeuwen CJ, Espeldoorn A and Mol F | Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo Gairdneri) | Aquatic Toxicology | 1986 | 2018/12/05 | |||||
| 魚類 | Brachydanio rerio (Zebrafish) | LC50 | 7 | days | 0.034 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Grootelaar EMM, and Niebeek G | Fish Embryos as Teratogenicity Screens : A Comparison of Embryotoxicity between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2018/12/05 | ||||||
| 魚類 | Brachydanio rerio (Zebrafish) | Mortality | LOEC | 7 | 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 | Van Leeuwen, C.J., E.M.M. Grootelaar, and G. Niebeek | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds. | Ecotoxicol.Environ.Saf. | 1990 | 2016/03/07 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | LOEC | 60 | days | 0.56 | 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 | Van Leeuwen, C.J., A. Espeldoorn, and F. Mol (1986) | Aquatic Toxicological Aspects of Dithiocarbamates and Related Compounds. III. Embryolarval Studies with Rainbow Trout (Salmo gairdneri). | Aquat.Toxicol. | 1986 | 2016/03/07 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | EC50 | 60 | days | 0.00064 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van leeuwen CJ, Espeldoorn A and Mol F | Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo Gairdneri) | Aquatic Toxicology | 1986 | 2016/02/22 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 60 | days | 0.0011 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van leeuwen CJ, Espeldoorn A and Mol F | Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo Gairdneri) | Aquatic Toxicology | 1986 | 2016/02/22 | ||||||
| 魚類 | Brachydanio rerio (Zebrafish) | mortality | LOEC | 7 | days | 0.001 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Grootelaar EMM, and Niebeek G | Fish Embryos as Teratogenicity Screens : A Comparison of Embryotoxicity between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2016/02/22 | |||||
| 魚類 | Brachydanio rerio (Zebrafish) | EC50 | 7 | days | 0.006 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Grootelaar EMM, and Niebeek G | Fish Embryos as Teratogenicity Screens : A Comparison of Embryotoxicity between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2016/02/22 | ||||||
| 魚類 | Brachydanio rerio (Zebrafish) | LC50 | 7 | days | 0.034 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van Leeuwen CJ, Grootelaar EMM, and Niebeek G | Fish Embryos as Teratogenicity Screens : A Comparison of Embryotoxicity between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2016/02/22 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | NOEC | 96 | hours | 0.076 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2016/02/22 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LOEC | 60 | days | 0.001 | mg/L | 4 OECD SIDS (HPVC) | 4 | Van leeuwen CJ, Espeldoorn A and Mol F | Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo Gairdneri) | Aquatic Toxicology | 1986 | 2016/02/22 | |||||
| 魚類 | Oryzias latipes (Japanese medaka) | LOEC | 96 | hours | 0.2 | mg/L | ○ | 4 OECD SIDS (HPVC) | 1 | National Institute of Environmental Research (NIER), Korea | Acute toxicity test of Bis (dimethylthiocarbamoyl) disulfide (CAS No.:137-26-8) in fish (Oryzias latipes) | 2008 | 2016/02/22 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | NOEL | 96 | hours | 100 | ppb | 3 USEPA Pesticide Ecotoxicity Database | McCann/Bascietto | 1972 | 2018/03/07 | |||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | EGGSLAID, SURVIVE | NOEL | 210 | days | 1.1 | ppb | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2011 | 2018/03/07 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | 11 | ppb | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2018/03/07 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | SURVIVE, GROWTH | NOEL | 28 | days | 15 | ppb | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2018/03/07 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | EGGSLAID, SURVIVE | LOEC | 210 | days | 2.2 | ppb | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2011 | 2018/03/07 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | SURVIVE, GROWTH | NOEL | 28 | days | 25 | ppb | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2018/03/07 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | SURVIVE, GROWTH | LC50 | 28 | days | 49.1 | ppb | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2018/03/07 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | SURVIVE, GROWTH | LOEC | 28 | days | 25 | ppb | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2018/03/07 | ||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | mortality | 96 | hours | <0.056 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2016/03/27 | |||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | NOEL | 96 | hours | 90 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | B. Montague | 1993 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | 42 | days | 0.02 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | 2016/03/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | 42 | days | 0.012 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | 2016/03/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | SURVIVE, GROWTH | NOEL | 28 | days | 25 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2016/02/02 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | growth rate | 28 | days | 0.02 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | 2016/03/18 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | number hatched | 33 | days | 9.3 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | 11 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | SURVIVE, GROWTH | NOEL | 28 | days | 15 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2016/02/02 | ||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | NOEL | 96 | hours | 32 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | J.J. Bascietto | 1983 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | 56 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | J.J. Bascietto | 1983 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 48 | hours | 32 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | J.McCann/Bascietto | 1983 | 2016/02/02 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | 96 | hours | 0.01 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2000 | 2016/03/18 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | EGGSLAID, SURVIVE | NOEL | 210 | days | 1.1 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2011 | 2016/02/02 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality and growth | 33 | days | 4.6 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | |||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality and growth | 33 | days | 9.3 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | NOEL | 96 | hours | 100 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | McCann/Bascietto | 1972 | 2016/02/02 | |||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | EGGSLAID, SURVIVE | LOEC | 210 | days | 2.2 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2011 | 2016/02/02 | ||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | SURVIVE, GROWTH | LOEC | 28 | days | 25 | μg/L | 3 USEPA Pesticide Ecotoxicity Database | N. Federoff | 2012 | 2016/02/02 | ||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | mortality | 96 | hours | 0.1 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1983 | 2016/03/18 | |||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | mortality | 96 | hours | 0.09 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1992 | 2016/03/18 |