【注意事項】
* 生態影響に係る有害性情報更新日が2019年9月以前はRead-acrossデータに○を記載しておらず、被験物質が標記の物質ではない可能性がある。
**各情報源における信頼性評価スコアの定義は下記のとおりである。
生物種 | 学名 | 影響内容 | エンドポイント | 暴露期間(値) | 暴露期間(単位) | 毒性値 | 毒性値(単位) | 毒性値(単位)種別 | 試験中の 被験物質 濃度測定 あり:○ なし:× |
情報源 | 情報源による 信頼性評価** |
著者 | タイトル | 記載誌 | 発行年 | 情報更新日 | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
subject type | scientific name | effect | endpoint | exposure duration value |
exposure duration unit |
toxicity value | toxicity unit | toxicity unit type | Read-across* | QSAR | GLP | measurement of the test material |
original work type | original work reliability rank |
author | title | referenced journal | publication year | Information update date |
藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 1700 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | In-Depth Studies on Health and Environmental Impacts of Selected Water Pollutants | U.S.EPA Contract No.68-01-4646, Duluth, MN:9 p. | 1978 | 2016/03/25 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.58 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
藻類 | Pseudokirchneriella subcapitata | decrease in chlorophyll a | EC50 | 48 | hours | >2.5~5 | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/22 | |||||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 0.405 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.455 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
藻類 | Pseudokirchneriella subcapitata | decrease in chlorophyll a | EC50 | 24 | hours | >10 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/22 | ||||||
藻類 | Pseudokirchneriella subcapitata | cell number | EC50 | 96 | hours | 2.5 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/22 | ||||||
藻類 | Pseudokirchneriella subcapitata | decrease in chlorophyll a | EC50 | 96 | hours | 2.5 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/22 | ||||||
藻類 | Pseudokirchneriella subcapitata | decrease in chlorophyll a | EC50 | 72 | hours | >2.5~5 | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/22 | |||||||
藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 0.304 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 0.41 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成27年3月版) | 2016/11/09 | |||||||||
藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 0.58 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成27年3月版) | 2016/11/09 | |||||||||
藻類 | Pseudokirchneriella subcapitata | biomass | NOEC | 72 | hours | 0.188 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
藻類 | Pseudokirchneriella subcapitata | biomass | NOEC | 72 | hours | 0.25 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 0.24 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 0.32 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 0.25 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成27年3月版) | 2016/11/09 | |||||||||
藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 0.32 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成27年3月版) | 2016/11/09 | |||||||||
甲殻類 | Daphnia magna | Mortality | LC50 | 1 | days | 1400 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | LeBlanc,G.A. | Acute Toxicity of Priority Pollutants to Water Flea (Daphnia magna) | Bull. Environ. Contam. Toxicol.24(5): 684-691 | 1980 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 670 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | LeBlanc,G.A. | Acute Toxicity of Priority Pollutants to Water Flea (Daphnia magna) | Bull. Environ. Contam. Toxicol.24(5): 684-691 | 1980 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | Mortality | NOEC | 2 | days | 410 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | LeBlanc,G.A. | Acute Toxicity of Priority Pollutants to Water Flea (Daphnia magna) | Bull. Environ. Contam. Toxicol.24(5): 684-691 | 1980 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 2.92 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
甲殻類 | Daphnia magna | mobility | EC100 | 48 | hours | 4.06 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 24 | hours | 2.2 | mg/L | × | 12 ECHA Information on Registered Substances | 1 | study report | 1980 | 2016/03/23 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 1.96 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 1.7 | mg/L | × | 12 ECHA Information on Registered Substances | 1 | study report | 1980 | 2016/03/23 | ||||||
甲殻類 | Daphnia magna | mobility | EC100 | 24 | hours | >4.06 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 2 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成27年3月版) | 2016/11/09 | |||||||||
甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 0.59 | 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 | mobility | 48 | hours | 0.76 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | |||||||
甲殻類 | Daphnia magna | mobility | NOEC | 24 | hours | 0.76 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2005 | 2016/03/23 | ||||||
甲殻類 | Daphnia magna | mortality | NOEC | 48 | hours | 1 | mg/L | × | 12 ECHA Information on Registered Substances | 1 | study report | 1980 | 2016/03/23 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | 1700 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | In-Depth Studies on Health and Environmental Impacts of Selected Water Pollutants | U.S.EPA Contract No.68-01-4646, Duluth, MN:9 p. | 1978 | 2016/03/25 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Accumulation | 8 | hours | 29 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wong,K., R.F. Addison, and F.C.P. Law | Uptake, Metabolism, and Elimination of Diphenyl Ether by Trout and Stickleback | Bull. Environ. Contam. Toxicol.26(2): 243-247 | 1981 | 2016/03/25 | |||||||
魚類 | Cyprinus carpio (Carp) | Mortality | 2.75 | days | 77~198 | 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 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 4000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Geiger,D.L., D.J. Call, and L.T. Brooke | Acute Toxicities of Organic Chemicals to Fathead Minnows (Pimephales promelas) Volume IV | Center for Lake Superior Environmental Studies, University of Wisconsin, Superior, WI4:355 p. | 1988 | 2016/03/25 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 5.3 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2016/03/23 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 13 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/23 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 48 | hours | 13 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/23 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 24 | hours | 34 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/23 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 48 | hours | 6 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/23 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | EC50 | 96 | hours | 2.5 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2016/03/23 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 4.2 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/23 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 24 | hours | 10 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/23 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Lethal | EC50 | 96 | hours | 4 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Veith ea 83 | 2016/02/08 | |||||||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 1.8 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成27年3月版) | 2016/11/09 | |||||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 48 | hours | 4.58 | 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 | Leuciscus idus (Orfe) | Mortality | LC50 | 96 | hours | 3.03 | 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 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 96 | hours | 3.99 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Russom, C.L., Bradbury, S.P., Broderius, S.J., Drummond, R.A. and Hammermeister, D.E. | PREDICTING MODES OF TOXIC ACTION FROM CHEMICAL STRUCTURE: ACUTE TOXICITY IN THE FATHEAD MINNOW (PIMEPHALES PROMELAS) | 1997 | 2016/02/08 | |||||||
魚類 | Poecilia reticulata (Guppy) | Mortality | LC50 | 96 | hours | 4.08 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Raevsky, O.A., and Dearden, J.C. | Creation of predictive models of aquatic toxicity of environmental pollutants with different mechanisms of action on the basis of molecular similarity and hybot descriptors. | 2004 | 2016/02/08 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | mortality and observations | NOEC | 96 | hours | 10 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/23 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | NOEC | 96 | hours | 3.2 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1980 | 2016/03/23 |