【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 | areas under the growth curves | EC50 | 72 | hours | 6.8 | mg/L | 12 ECHA Information on Registered Substances | 2 | data published | 1999 | 2017/01/21 | |||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 96 | hours | 24.82 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC50 | 96 | hours | 15.136 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC50 | 72 | hours | 22 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC50 | 96 | hours | 15.136 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 72 | hours | 22.4 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC50 | 72 | hours | 22 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 8 | mg/L | 12 ECHA Information on Registered Substances | 2 | data published | 1999 | 2017/01/21 | |||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 72 | hours | 22.4 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 96 | hours | 24.82 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 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28年3月版) | 2016 | 2016/11/08 | ||||||||
藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 6.8 | 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28年3月版) | 2016 | 2016/11/08 | ||||||||
藻類 | Selenastrum capricornutum | 生長曲線下面積 | EbC50 | 72 | hours | 6.75 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
藻類 | Pseudokirchneriella subcapitata | Growth:生長(速度法) | EC50 | 3 | days | 7970 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | (独)国立環境研究所 | 平成17 年度化学物質環境リスク評価検討調査報告書 | 2006 | 2017/01/23 | ||||||
藻類 | Selenastrum capricornutum | 生長速度 | ErC50 | 72 | hours | 8.55 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
藻類 | Selenastrum capricornutum | 生長速度 | ErC50 | 48 | hours | 9.06 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
藻類 | Pseudokirchneriella subcapitata | Growth:生長(面積法) | EC50 | 3 | days | 6750 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | 環境庁 | 平成11 年度 生態影響試験 | 2000 | 2017/01/23 | ||||||
藻類 | Selenastrum capricornutum | 生長速度 | NOErC | 72 | hours | 1.27 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
藻類 | Pseudokirchneriella subcapitata | areas under the growth curves | NOEC | 72 | hours | 1.8 | mg/L | 12 ECHA Information on Registered Substances | 2 | data published | 1999 | 2017/01/21 | |||||||
藻類 | Desmodesmus subspicatus | biomass | EC10 | 96 | hours | 3.317 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC10 | 96 | hours | 10.462 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC10 | 72 | hours | 4.77 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC10 | 96 | hours | 3.317 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC10 | 72 | hours | 9.026 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC10 | 96 | hours | 10.462 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | growth rate | EC10 | 72 | hours | 9.026 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Desmodesmus subspicatus | biomass | EC10 | 72 | hours | 4.77 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1989 | 2017/01/21 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 1.1 | mg/L | 12 ECHA Information on Registered Substances | 2 | data published | 1999 | 2017/01/21 | |||||||
藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 1.1 | 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28年3月版) | 2016 | 2016/11/08 | ||||||||
藻類 | Pseudokirchneriella subcapitata | Growth:生長(速度法) | NOEC | 3 | days | 1100 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | (独)国立環境研究所 | 平成17 年度化学物質環境リスク評価検討調査報告書 | 2006 | 2017/01/23 | ||||||
藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | 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28年3月版) | 2016 | 2016/11/08 | ||||||||
藻類 | Selenastrum capricornutum | 生長曲線下面積 | NOEbC | 72 | hours | 1.82 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
藻類 | Selenastrum capricornutum | 生長速度 | NOErC | 48 | hours | 5.26 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
藻類 | Pseudokirchneriella subcapitata | Growth:生長(面積法) | NOEC | 3 | days | 1820 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | 環境庁 | 平成11 年度 生態影響試験 | 2000 | 2017/01/23 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 24 | hours | 62.8 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC100 | 48 | hours | 105 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC100 | 24 | hours | 105 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
甲殻類 | Ceriodaphnia dubia | mobility | EC50 | 48 | hours | 17 | mg/L | 12 ECHA Information on Registered Substances | 3 | study report | 1995 | 2017/01/21 | |||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 200 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | Bringmann, G. and Kuhn, R. | The Toxic Effects of Waste Water on Aquatic Bacteria, Algae, and Small Crustaceans | Gesund Ing | 1959 | 2017/01/21 | |||||
甲殻類 | Ceriodaphnia dubia | mortality | EC50 | 48 | hours | 17 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | Bannister RM, Bettncourt MJ, Collins MK and, Kendall TZ. | Acute and chronic toxicity of alkylamines to Ceridaphnia dubia and rainbow trout. | Society of Toxicology Meeting Baltimore, MD | 1995 | 2017/01/21 | ||||
甲殻類 | Ceriodaphnia dubia | mortality | LC50 | 48 | hours | 17 | mg/L | act. ingr. | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1994 | 2017/02/27 | |||||
甲殻類 | Daphnia magna | behaviour | EC50 | 48 | hours | 200 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | Bringmann, G. and Kuhn, R. | The Toxic Effects of Waste Water on Aquatic Bacteria, Algae, and Small Crustaceans | Gesund Ing | 1959 | 2017/01/21 | ||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 34 | mg/L | 12 ECHA Information on Registered Substances | 2 | data published | 1999 | 2017/01/21 | ||||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 200 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 | |||||||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 34 | 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28年3月版) | 2016 | 2016/11/08 | ||||||||
甲殻類 | Daphnia magna | Immobilization:遊泳阻害 | EC50 | 2 | days | 34000 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | 環境庁 | 平成11 年度 生態影響試験 | 2000 | 2017/01/23 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 48 | hours | 34 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
甲殻類 | Ceriodaphnia dubia | EC50 | 48 | hours | 17 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 | |||||||||||
甲殻類 | Daphnia magna | 遊泳阻害 | NOEC | 24 | hours | 16.9 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
甲殻類 | Ceriodaphnia dubia | mortality | 7 | days | 10 | × | 12 ECHA Information on Registered Substances | 3 | Bannister RM, Bettencourt MJ, Collins MK and Kendall TZ | Acute and chronic toxicity of alkylamines to Ceridaphnia dubia and rainbow trout. | Society of Toxicology Meeting Baltimore, MD | 1995 | 2017/01/21 | ||||||
甲殻類 | Ceriodaphnia dubia | adverse physical or behavioural effects | NOEC | 48 | hours | 12 | mg/L | act. ingr. | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1994 | 2017/02/27 | |||||
甲殻類 | Ceriodaphnia dubia | reproduction | LOEC | 7 | days | 14 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1994 | 2017/01/21 | ||||||
甲殻類 | Ceriodaphnia dubia | reproduction | NOEC | 7 | days | 7.1 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1994 | 2017/01/21 | ||||||
甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 38 | mg/L | 12 ECHA Information on Registered Substances | 2 | data published | 1999 | 2017/01/21 | |||||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 11 | mg/L | 12 ECHA Information on Registered Substances | 2 | data published | 1999 | 2017/01/21 | |||||||
甲殻類 | Ceriodaphnia dubia | reproduction | 7 | days | 10 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 1994 | 2017/01/21 | |||||||
甲殻類 | Daphnia magna | NOEC | 21 | days | 11 | 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28年3月版) | 2016 | 2016/11/08 | ||||||||
甲殻類 | Daphnia magna | EC50 | 21 | days | 38 | 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28年3月版) | 2016 | 2016/11/08 | ||||||||
甲殻類 | Ceriodaphnia dubia | NOEC | 7 | days | 7.1 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/13 | |||||||||||
甲殻類 | Daphnia magna | LOEC | 21 | days | 23.4 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | |||||||||||
甲殻類 | Daphnia magna | Reproduction:繁殖、再生産 | NOEC | 21 | days | 10700 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | B | 環境庁 | 平成11 年度 生態影響試験 | 2000 | 2017/01/23 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | NOEC | 48 | hours | 11.6 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
甲殻類 | Daphnia magna | NOEC | 21 | days | 10.7 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | |||||||||||
甲殻類 | Daphnia magna | LC50 | 21 | days | >52.7 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | |||||||||||
甲殻類 | Daphnia magna | 繁殖阻害 | EC50 | 21 | days | 38.4 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | ||||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LOEC | 60 | days | >100000 | 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 | 2017/03/15 | |||||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 7 | days | 180000 | 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 | 2017/03/15 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 1 | days | 1000000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tonogai,Y., S. Ogawa, Y. Ito, and M. Iwaida | Actual Survey on TLM (Median Tolerance Limit) Values of Environmental Pollutants, Especially on Amines, Nitriles, Aromatic Nitrogen Compounds | J. Toxicol. Sci.7(3): 193-203 | 1982 | 2017/03/15 | ||||||
魚類 | Danio rerio (Zebrafish) | Growth | EC50 | 7 | days | 53000 | 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 | 2017/03/15 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | LOEC | 60 | days | 100000 | 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 | 2017/03/15 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | EC50 | 60 | days | 130000 | 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 | 2017/03/15 | ||||||
魚類 | Danio rerio (Zebrafish) | LOEC | 7 | days | 100000 | 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 | 2017/03/15 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 2 | days | 720000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Tonogai,Y., S. Ogawa, Y. Ito, and M. Iwaida | Actual Survey on TLM (Median Tolerance Limit) Values of Environmental Pollutants, Especially on Amines, Nitriles, Aromatic Nitrogen Compounds | J. Toxicol. Sci.7(3): 193-203 | 1982 | 2017/03/15 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LOEC | 60 | days | >100000 | 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 | 2017/03/15 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 60 | days | 137000 | 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 | 2017/03/15 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality | LOEC | 7 | days | 320000 | 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 | 2017/03/15 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth | LOEC | 60 | days | 3200 | 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 | 2017/03/15 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 48 | hours | 720000 | μg/L | 12 ECHA Information on Registered Substances | 4 | TONOGAI, Y.; S. OGAWA; Y. ITO; M. IWAIDA | Actual Survey on TLM (Median Tolerance Limit) Values of Environmental Pollutants, Especially on Amines, Nitriles, Aromatic Nitrogen Compounds | Journal of Toxicological Sciences | 1982 | 2017/01/21 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 38 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | Bannister RM, Bettencourt MJ, Collins MK and Kandell TZ | Acute and Chronic toxicity of alkylamines to Ceriodaphnia dubia and rainbow trout. | Society of Toxicology Meeting, Baltimore MD. | 1995 | 2017/01/21 | ||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 38 | mg/L | 12 ECHA Information on Registered Substances | 3 | study report | 1995 | 2017/02/27 | |||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 24 | hours | 100000 | μg/L | 12 ECHA Information on Registered Substances | 4 | TONOGAI, Y.; S. OGAWA; Y. ITO; M. IWAIDA | Actual Survey on TLM (Median Tolerance Limit) Values of Environmental Pollutants, Especially on Amines, Nitriles, Aromatic Nitrogen Compounds | Journal of Toxicological Sciences | 1982 | 2017/01/21 | |||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 24 | mg/L | 12 ECHA Information on Registered Substances | 2 | data published | 1999 | 2017/01/21 | ||||||||
魚類 | Leuciscus idus (Orfe) | mortality | LC50 | 48 | hours | >500 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1977 | 2017/01/21 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 36 | mg/L | act. ingr. | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1994 | 2017/02/27 | |||||
魚類 | Danio rerio (Zebrafish) | LC50 | 7 | days | 180 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 | |||||||||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 24 | 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28年3月版) | 2016 | 2016/11/08 | ||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 36 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 | |||||||||||
魚類 | Danio rerio (Zebrafish) | total embrytoxicity | EC50 | 96 | hours | 53 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 | ||||||||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 24 | mg/L | 11 Japan チャレンジプログラム | 2017/01/23 | |||||||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality:死亡 | 2 | 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 | Tonogai, Y., S. Ogawa, Y. Ito, and M. Iwaida | Actual Survey on TLm (Median Tolerance Limit) Values of Environmental Pollutants, Especially on Amines, Nitriles, Aromatic Nitrogen Compounds. | J.Toxicol.Sci. | 1982 | 2017/01/23 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality:死亡 | LC50 | 4 | days | 24000 | μg/L | 6 日本環境省 化学物質の環境リスク評価(生態リスク初期評価) | A | 環境庁 | 平成11 年度 生態影響試験 | 2000 | 2017/01/23 | ||||||
魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 48 | hours | 50.7 | mg/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 | 2017/03/22 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LOEC | 60 | days | >100 | mg/L | 12 ECHA Information on Registered Substances | 2 | Van Leeuwen, C.J., Grootelaar, E.M.M., Niebeek, G. | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2017/01/21 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | weight | LOEC | 60 | days | 3.2 | mg/L | 12 ECHA Information on Registered Substances | 2 | Van Leeuwen, C.J., Grootelaar, E.M.M., Niebeek, G. | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2017/01/21 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 60 | days | 137 | mg/L | 12 ECHA Information on Registered Substances | 2 | Van Leeuwen, C.J., Grootelaar, E.M.M., Niebeek, G. | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2017/01/21 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | EC50 | 60 | days | 130 | mg/L | 12 ECHA Information on Registered Substances | 2 | Van Leeuwen, C.J., Grootelaar, E.M.M., Niebeek, G. | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2017/01/21 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEC | 96 | hours | 16 | mg/L | act. ingr. | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 1994 | 2017/02/27 | ||||||
魚類 | Danio rerio (Zebrafish) | total embryotoxicity | LOEC | 7 | days | 100 | mg/L | 12 ECHA Information on Registered Substances | 2 | Van Leeuwen, C.J., Grootelaar, E.M.M., Niebeek, G. | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2017/02/27 | |||||
魚類 | Danio rerio (Zebrafish) | mortality | LOEC | 7 | days | 320 | mg/L | 12 ECHA Information on Registered Substances | 2 | Van Leeuwen, C.J., Grootelaar, E.M.M., Niebeek, G. | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2017/02/27 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | length | LOEC | 60 | days | 100 | mg/L | 12 ECHA Information on Registered Substances | 2 | Van Leeuwen, C.J., Grootelaar, E.M.M., Niebeek, G. | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2017/01/21 | |||||
魚類 | Danio rerio (Zebrafish) | total embryotoxicity | EC50 | 7 | days | 53 | mg/L | 12 ECHA Information on Registered Substances | 2 | Van Leeuwen, C.J., Grootelaar, E.M.M., Niebeek, G. | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2017/02/27 | |||||
魚類 | Danio rerio (Zebrafish) | mortality | LC50 | 7 | days | 180 | mg/L | 12 ECHA Information on Registered Substances | 2 | Van Leeuwen, C.J., Grootelaar, E.M.M., Niebeek, G. | Fish Embryos as Teratogenicity Screens: A Comparison of Embryotoxicity Between Fish and Birds | Ecotoxicology and Environmental Safety | 1990 | 2017/02/27 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | body weight | LOEC | 60 | days | 3.2 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 | ||||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Growth:成長 | NOEC | 60 | days | <3200 | 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 | 2017/01/23 | |||||
魚類 | Danio rerio (Zebrafish) | total embrytoxicity | LOEC | 96 | hours | 100 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/13 | ||||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | total embryotoxicity | LOEC | 60 | days | >100 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 | ||||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LOEC | 60 | days | >100 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 | ||||||||||
魚類 | Danio rerio (Zebrafish) | mortality | LOEC | 96 | hours | 320 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 | ||||||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | body length | LOEC | 60 | days | 100 | mg/L | 4 OECD SIDS (HPVC) | 2017/03/12 |