【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 | Pseudokirchneriella subcapitata | growth rate | EC50 | 48 | hours | >=18 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
藻類 | Selenastrum capricornutum | 生長曲線下面積 | EbC50 | 72 | hours | >=18 | mg/L | ○ | 対照区, 助剤対照区, 1.8, 3.2, 5.6, 10, 18mg/l | 0, 0.372, 0.669, 1.75, 2.20, 3.57mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
藻類 | Selenastrum capricornutum | 生長速度 | EC50 | 72 | hours | >3.57 | mg/L | ○ | 対照区, 助剤対照区, 1.8, 3.2, 5.6, 10, 18mg/l | 0, 0.372, 0.669, 1.75, 2.20, 3.57mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | ErC50 | 72 | hours | >3.6 | mg/L | 0, 1.8, 3.2, 5.6, 10, 18mg/l | 0, 0.37, 0.67, 1.75, 2.2, 3.6mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート(三監No.8) | 2020/01/08 | ||||||
藻類 | Chlorella pyrenoidosa | Growth | EC50 | 2 | days | 3800 | 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 | Canton, J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms. | Water Res. 17(7) | 1983 | 2020/02/14 | |||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | >=18 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | EC50 | 3 | days | >3570 | 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 | (独)国立環境研究所 | 平成17 年度化学物質環境リスク評価検討調査報告書 | 2006 | 2020/02/14 | ||||||
藻類 | Pseudokirchneriella subcapitata | other: Areas under growth curve | EC50 | 72 | hours | >=18 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
藻類 | Chlorella pyrenoidosa | PopulationPopulation change (change in N/change in time) | EC50 EC50 | 48 | hours | 3800 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
藻類 | Chlorella pyrenoidosa | PopulationPopulation change (change in N/change in time) | EC50 EC50 | 24 | hours | 48000 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | NOEC | 3 | days | 3570 | 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 | (独)国立環境研究所 | 平成17 年度化学物質環境リスク評価検討調査報告書 | 2006 | 2020/02/14 | ||||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | NOEC | 72 | hours | 0.67 | mg/L | 0, 1.8, 3.2, 5.6, 10, 18mg/l | 0, 0.37, 0.67, 1.75, 2.2, 3.6mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート(三監No.8) | 2020/01/08 | ||||||
藻類 | Selenastrum capricornutum | 生長速度 | NOEC | 72 | hours | 3.57 | mg/L | ○ | 対照区, 助剤対照区, 1.8, 3.2, 5.6, 10, 18mg/l | 0, 0.372, 0.669, 1.75, 2.20, 3.57mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
藻類 | Selenastrum capricornutum | 生長曲線下面積 | NOEbC | 72 | hours | 18 | mg/L | ○ | 対照区, 助剤対照区, 1.8, 3.2, 5.6, 10, 18mg/l | 0, 0.372, 0.669, 1.75, 2.20, 3.57mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 48 | hours | 1.8 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
藻類 | Pseudokirchneriella subcapitata | other: Areas under growth curve | NOEC | 72 | hours | 18 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
藻類 | Scenedesmus quadricauda | PopulationPopulation growth rate | LOEC LOEC | >400000 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bringmann,G., and R. Kuhn | Limiting Values for the Noxious Effects of Water Pollutant Material to Blue Algae (Microcystis aeruginosa) and Green Algae (Scenedesmus quadricauda) in Cell Propagation Inhibition Tests (Grenzwerte der Schadwirkung Wass | TR-80-0201, Literature Research Company, Annandale, VA | 1978 | |||||||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 1 | days | 720000 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | C | Bringmann, G., and R. Kühn | Results of Toxic Action of Water Pollutants on Daphnia magna Straus Tested by an Improved Standardized Procedure. | Z.Wasser-Abwasser-Forsch. 15(1) | 1982 | 2020/02/14 | |||||
甲殻類 | Daphnia magna | mobility | NOEC | 24 | hours | 1.9 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 2 | days | 2100 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | 環境省 | 平成12 年度生態影響試験 | 2001 | 2020/02/14 | ||||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 2 | days | 5300 | 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 | Canton, J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms. | Water Res. 17(7) | 1983 | 2020/02/14 | |||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 2.1 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.914, 1.49, 1.94, 2.46, 3.56, 5.64, 7.42mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
甲殻類 | Daphnia magna | Immobilization | EC100 | 24 | hours | 5.6 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.914, 1.49, 1.94, 2.46, 3.56, 5.64, 7.42mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
甲殻類 | Daphnia magna | Immobilization | NOEC | 24 | hours | 1.9 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.914, 1.49, 1.94, 2.46, 3.56, 5.64, 7.42mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 24 | hours | 2.6 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.914, 1.49, 1.94, 2.46, 3.56, 5.64, 7.42mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 2.6 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
甲殻類 | Daphnia magna | Immobilization | NOEC | 48 | hours | 1.5 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.914, 1.49, 1.94, 2.46, 3.56, 5.64, 7.42mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
甲殻類 | Daphnia magna | immobilization | EC0 | 48 | hours | 1.5 | mg/L | 0, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.914, 1.49, 1.94, 2.46, 3.56, 5.64, 7.42mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート(三監No.8) | 2020/01/08 | ||||||
甲殻類 | Daphnia magna | Immobilization | EC100 | 48 | hours | 2.5 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.914, 1.49, 1.94, 2.46, 3.56, 5.64, 7.42mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
甲殻類 | Daphnia magna | mobility | NOEC | 48 | hours | 1.5 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
甲殻類 | Daphnia magna | immobilization | EC50 | 48 | hours | 2.1 | mg/L | 0, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.914, 1.49, 1.94, 2.46, 3.56, 5.64, 7.42mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート(三監No.8) | 2020/01/08 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 2.1 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
甲殻類 | Mortality | LC50 | 48 | hours | 0.115 | 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 | ||||||||
甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50/ | 48 | hours | 5300 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
甲殻類 | Daphnia magna | IntoxicationImmobile | LC50 LC50 | 24 | hours | >50 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bringmann,G., and R. Kuhn | Results of the Damaging Effect of Water Pollutants on Daphnia magna (Befunde der Schadwirkung Wassergefahrdender Stoffe Gegen Daphnia magna) | TR-79-1204, Literature Research Company, Annandale, VA | 1977 | |||||||
甲殻類 | Crassostrea gigas | MultipleMultiple effects reported as one result | 48 | hours | 691 | μL/L [Formulation] | 0 ul/L / >100-<10000 ul/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Legore,R.S. | The Effect of Alaskan Crude Oil and Selected Hydrocarbon Compounds on Embryonic Development of the Pacific Oyster, Crassostrea gigas | Ph.D. Thesis, University of Washington, Seattle, WA | 1974 | |||||||
甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 9400 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
甲殻類 | Crassostrea gigas | DevelopmentAbnormal | 48 | hours | 1701 | μL/L [Formulation] | 0 ul/L / >100-<10000 ul/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Legore,R.S. | The Effect of Alaskan Crude Oil and Selected Hydrocarbon Compounds on Embryonic Development of the Pacific Oyster, Crassostrea gigas | Ph.D. Thesis, University of Washington, Seattle, WA | 1974 | |||||||
甲殻類 | Daphnia magna | Mortality | LC50 | 21 | days | 1.4 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.27, 0.53, 0.74, 1.17, 1.75, 3.02, 3.97mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 0.74 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.27, 0.53, 0.74, 1.17, 1.75, 3.02, 3.97mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
甲殻類 | Daphnia magna | Reproduction | LOEC | 21 | days | 1.2 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.27, 0.53, 0.74, 1.17, 1.75, 3.02, 3.97mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
甲殻類 | Daphnia magna | Reproduction | EC50 | 21 | days | 1 | mg/L | ○ | 対照区, 助剤対照区, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.27, 0.53, 0.74, 1.17, 1.75, 3.02, 3.97mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 0.74 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
甲殻類 | Daphnia magna | reproduction | LOEC | 21 | days | 1.2 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 740 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | 環境省 | 平成12 年度生態影響試験 | 2001 | 2020/02/14 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 21 | days | 1.4 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 15 | days | 2400 | 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 | Canton, J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms. | Water Res. 17(7) | 1983 | 2020/02/14 | |||||
甲殻類 | Daphnia magna | mortality | EC50 | 21 | days | 1 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 0.74 | mg/L | 0, 1.0, 1.5, 2.2, 3.2, 4.6, 6.8, 10mg/l | 0.27, 0.53, 0.74, 1.17, 1.75, 3.02, 3.97mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート(三監No.8) | 2020/01/08 | ||||||
甲殻類 | Daphnia magna | ReproductionReproduction, general | EC50 EC50 | 15 | days | 2900 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 15 | days | 4000 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
魚類 | Poecilia reticulata (Guppy) | BehaviorBehavioral changes, general | EC50 EC50/ | 24 | hours | 4500 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
魚類 | Poecilia reticulata (Guppy) | BehaviorBehavioral changes, general | EC50 EC50/ | 96 | hours | 4500 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
魚類 | Poecilia reticulata (Guppy) | BehaviorBehavioral changes, general | EC50 EC50/ | 72 | hours | 4500 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
魚類 | Poecilia reticulata (Guppy) | BehaviorBehavioral changes, general | EC50 EC50/ | 48 | hours | 4500 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 96 | hours | 5.8 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC100 | 72 | hours | 16.6 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC100 | 96 | hours | 16.6 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | 5.8 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC0 | 96 | hours | 4 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 4 | days | 5800 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | 環境省 | 平成12 年度生態影響試験 | 2001 | 2020/02/14 | ||||||
魚類 | Poecilia reticulata (Guppy) | Mortality | LC50 | 4 | days | 7100 | 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 | Canton, J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms. | Water Res. 17(7) | 1983 | 2020/02/14 | |||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC100 | 96 | hours | 17 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2001 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 48 | hours | 5.8 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Mortality | LC50 | 96 | hours | 0.479 | 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 | ||||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | 5.8 | mg/L | 0, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート(三監No.8) | 2020/01/08 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC0 | 96 | hours | 4 | mg/L | 0, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート(三監No.8) | 2020/01/08 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC0 | 72 | hours | 4.02 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC0 | 96 | hours | 4.02 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 24 | hours | 5.8 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 72 | hours | 5.8 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC0 | 24 | hours | 4.02 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC100 | 48 | hours | 16.6 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC0 | 48 | hours | 4.02 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC100 | 24 | hours | 16.6 | mg/L | ○ | 対照区, 助剤対照区, 3.2, 4.2, 5.6, 7.5, 10, 13, 18mg/l | 2.27, 2.77, 4.02, 5.78, 7.77, 10.7, 16.6mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
魚類 | Poecilia reticulata (Guppy) | MortalityMortality | LC50 LC50 | 24 | hours | 12200 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
魚類 | Poecilia reticulata (Guppy) | MortalityMortality | LC50 LC50 | 48 | hours | 10600 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
魚類 | Poecilia reticulata (Guppy) | MortalityMortality | LC50 LC50 | 96 | hours | 7100 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
魚類 | Poecilia reticulata (Guppy) | MortalityMortality | LC50 LC50 | 72 | hours | 8700 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H., and R.C.C. Wegman | Studies on the Toxicity of Tribromoethene, Cyclohexene and Bromocyclohexane to Different Freshwater Organisms | Water Res.17(7) | 1983 | |||||||
その他 | Development, Mortality | EC50 | 2 | days | 560000 | 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 | Legore, R.S. | The Effect of Alaskan Crude Oil and Selected Hydrocarbon Compounds on Embryonic Development of the Pacfic Oyster, Crassostrea gigas. | Ph.D.Thesis, Univ.of Washington, Seattle, WA | 1974 | 2020/02/14 |