【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 | 2 | days | 270700 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lee,P.Y., and C.Y. Chen | Toxicity and Quantitative Structure-Activity Relationships of Benzoic Acids to Pseudokirchneriella subcapitata | J. Hazard. Mater.165(1-3): 156-161 | 2009 | 2017/03/15 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 2 | days | 179900 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lee,P.Y., and C.Y. Chen | Toxicity and Quantitative Structure-Activity Relationships of Benzoic Acids to Pseudokirchneriella subcapitata | J. Hazard. Mater.165(1-3): 156-161 | 2009 | 2017/03/15 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 3 | days | >1000 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2017/03/15 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 2 | days | 179900 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lee,P.Y., and C.Y. Chen | Toxicity and Quantitative Structure-Activity Relationships of Benzoic Acids to Pseudokirchneriella subcapitata | J. Hazard. Mater.165(1-3): 156-161 | 2009 | 2017/03/15 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 2 | days | 355000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lee,P.Y., and C.Y. Chen | Toxicity and Quantitative Structure-Activity Relationships of Benzoic Acids to Pseudokirchneriella subcapitata | J. Hazard. Mater.165(1-3): 156-161 | 2009 | 2017/03/15 | ||||||
藻類 | Chlorella sp. Chlorella pyrenoidosa | Population | EC50 | 5 | days | >55200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Larson,L.J. | The Influence of Test Length and Bacteria on the Results of Algal Bioassays with Monophenolic Acids | ASTM Spec. Tech. Publ.2:230-239 | 1991 | 2017/03/15 | ||||||
藻類 | Chlorella sp. Chlorella pyrenoidosa | Population | EC50 | 2 | days | 30400 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Larson,L.J. | The Influence of Test Length and Bacteria on the Results of Algal Bioassays with Monophenolic Acids | ASTM Spec. Tech. Publ.2:230-239 | 1991 | 2017/03/15 | ||||||
藻類 | Chlorella sp. Chlorella pyrenoidosa | Population | EC50 | 4 | days | 42800 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Larson,L.J. | The Influence of Test Length and Bacteria on the Results of Algal Bioassays with Monophenolic Acids | ASTM Spec. Tech. Publ.2:230-239 | 1991 | 2017/03/15 | ||||||
藻類 | Chlorella sp. Chlorella pyrenoidosa | Population | EC50 | 5 | days | >55200 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Larson,L.J. | The Influence of Test Length and Bacteria on the Results of Algal Bioassays with Monophenolic Acids | ASTM Spec. Tech. Publ.2:230-239 | 1991 | 2017/03/15 | ||||||
藻類 | Chlorella sp. Chlorella pyrenoidosa | Population | EC50 | 1 | days | 34500 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Larson,L.J. | The Influence of Test Length and Bacteria on the Results of Algal Bioassays with Monophenolic Acids | ASTM Spec. Tech. Publ.2:230-239 | 1991 | 2017/03/15 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population | IC50 | 3 | days | >1000 | μM | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., T. Takada, and K. Suzuki | Effect of Medium Phosphate Levels on the Sensitivity of Selenastrum capricornutum to Chemicals | Bull. Environ. Contam. Toxicol.73(6): 995-1000 | 2004 | 2016/03/25 | ||||||
藻類 | Chlorella vulgaris | Population | 0.00005~0.001 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dedonder,A., and C.F. Van Sumere | The Effect of Phenolics and Related Compounds on the Growth and Respiration of Chlorella vulgaris | Z. Pflanzenphysiol.65:70-80 | 1971 | 2016/03/25 | ||||||||||
藻類 | Chlorella vulgaris | Physiology | 5 | hours | 0.00005~0.001 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dedonder,A., and C.F. Van Sumere | The Effect of Phenolics and Related Compounds on the Growth and Respiration of Chlorella vulgaris | Z. Pflanzenphysiol.65:70-80 | 1971 | 2016/03/25 | ||||||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 72 | hours | >1000 | mg/L | test with pH adjustment to pH 7.03 to 7.7 | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2009 | 2017/02/27 | |||||
藻類 | Chlorella sp. | reduction in growth | EC50 | 96 | hours | 42.8 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | Larson, L. | The influence of test length and bacteria on the results of algal bioassays with monophenolic acids | Plants for toxicity assessment: second volume, ASTM STP 1115, Gorsuch, J.W.; Lower, W.R:; Wang, W.; Lewis, M.A. eds. American Society for Testing and Materials, Philadelphia, 1991 | 1991 | 2017/02/27 | ||||
藻類 | Selenastrum capricornutum | biomass | EC50 | 48 | hours | 68.5 | mg/L | ○ | 4 OECD SIDS (HPVC) | Environment Agency of Japan | 1995 | 2017/02/06 | |||||||
藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 69 | 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 | 110 | 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 | Chlorella sp. | reduction in growth | EC50 | 120 | hours | >55.2 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | Larson, L. | The influence of test length and bacteria on the results of algal bioassays with monophenolic acids | Plants for toxicity assessment: second volume, ASTM STP 1115, Gorsuch, J.W.; Lower, W.R:; Wang, W.; Lewis, M.A. eds. American Society for Testing and Materials, Philadelphia, 1991 | 1991 | 2017/02/27 | ||||
藻類 | Selenastrum capricornutum | biomass | EC50 | 72 | hours | 68.5 | mg/L | area under the growth curve, test without pH adjustment | ○ | 12 ECHA Information on Registered Substances | 2 | published study report | 1997 | 2017/02/27 | |||||
藻類 | Desmodesmus subspicatus | growth rate | EC50 | 72 | hours | 92 | mg/L | test without pH adjustment, pH at EC50 = 5.8 | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2009 | 2017/02/27 | |||||
藻類 | Chlorella sp. | reduction in growth | EC50 | 24 | hours | 34.5 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | Larson, L. | The influence of test length and bacteria on the results of algal bioassays with monophenolic acids | Plants for toxicity assessment: second volume, ASTM STP 1115, Gorsuch, J.W.; Lower, W.R:; Wang, W.; Lewis, M.A. eds. American Society for Testing and Materials, Philadelphia, 1991 | 1991 | 2017/02/27 | ||||
藻類 | Selenastrum capricornutum | growth rate | EC50 | 72 | hours | 93.89 | mg/L | test without pH adjustment | ○ | 12 ECHA Information on Registered Substances | 2 | published study report | 1997 | 2017/02/27 | |||||
藻類 | Chlorella sp. | reduction in growth | EC50 | 48 | hours | 30.4 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | Larson, L. | The influence of test length and bacteria on the results of algal bioassays with monophenolic acids | Plants for toxicity assessment: second volume, ASTM STP 1115, Gorsuch, J.W.; Lower, W.R:; Wang, W.; Lewis, M.A. eds. American Society for Testing and Materials, Philadelphia, 1991 | 1991 | 2017/02/27 | ||||
藻類 | Selenastrum capricornutum | biomass | NOEC | 48 | hours | 32 | mg/L | ○ | 4 OECD SIDS (HPVC) | Environment Agency of Japan | 1995 | 2017/02/06 | |||||||
藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 51 | 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 | NOEC | 72 | hours | 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28年3月版) | 2016 | 2016/11/10 | ||||||||
藻類 | Desmodesmus subspicatus | growth rate | EC10 | 72 | hours | 249 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2009 | 2017/02/27 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 1690000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., Y. Fukaya, and K. Suzuki | Acute Toxicity of Benzoic Acids to the Crustacean Daphnia magna | Chemosphere59(2): 255-261 | 2005 | 2017/03/15 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 1 | days | 2720000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., Y. Fukaya, and K. Suzuki | Acute Toxicity of Benzoic Acids to the Crustacean Daphnia magna | Chemosphere59(2): 255-261 | 2005 | 2017/03/15 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 173000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kuhn,R., M. Pattard, K.D. Pernak, and A. Winter | Results of the Harmful Effects of Selected Water Pollutants (Anilines, Phenols, Aliphatic Compounds) to Daphnia magna | Water Res.23(4): 495-499 | 1989 | 2017/03/15 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 1 | days | 181000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kuhn,R., M. Pattard, K.D. Pernak, and A. Winter | Results of the Harmful Effects of Selected Water Pollutants (Anilines, Phenols, Aliphatic Compounds) to Daphnia magna | Water Res.23(4): 495-499 | 1989 | 2017/03/15 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 1690000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., Y. Fukaya, and K. Suzuki | Acute Toxicity of Benzoic Acids to the Crustacean Daphnia magna | Chemosphere59(2): 255-261 | 2005 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 1 | days | 2720000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kamaya,Y., Y. Fukaya, and K. Suzuki | Acute Toxicity of Benzoic Acids to the Crustacean Daphnia magna | Chemosphere59(2): 255-261 | 2005 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 173000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kuhn,R., M. Pattard, K.D. Pernak, and A. Winter | Results of the Harmful Effects of Selected Water Pollutants (Anilines, Phenols, Aliphatic Compounds) to Daphnia magna | Water Res.23(4): 495-499 | 1989 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 1 | days | 181000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kuhn,R., M. Pattard, K.D. Pernak, and A. Winter | Results of the Harmful Effects of Selected Water Pollutants (Anilines, Phenols, Aliphatic Compounds) to Daphnia magna | Water Res.23(4): 495-499 | 1989 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 1690 | mg/L | test with pH adjustment to pH 7.5 | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2017/02/27 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 2720 | mg/L | test with pH adjustment to pH 7.5 | 12 ECHA Information on Registered Substances | 2 | publication | 2005 | 2017/02/27 | ||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 135.7 | mg/L | ○ | 4 OECD SIDS (HPVC) | Environment Agency of Japan | 1995 | 2017/02/06 | ||||||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 140 | 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 | mobility | EC50 | 48 | hours | 136 | mg/L | test without pH neutralization | ○ | 12 ECHA Information on Registered Substances | 2 | published study report | 1997 | 2017/02/27 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 173 | mg/L | test with pH values not below pH 7.0 | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 1989 | 2017/02/27 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 67 | mg/L | test without pH-adjustment | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2009 | 2017/02/27 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 90 | mg/L | test without pH-adjustment | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2009 | 2017/02/27 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | >1000 | mg/L | test with pH adjustment | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2009 | 2017/02/27 | |||||
甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 136 | mg/L | test without pH neutralization | ○ | 12 ECHA Information on Registered Substances | 2 | published study report | 1997 | 2017/02/27 | |||||
甲殻類 | Daphnia magna | EC50 | 21 | days | >91 | 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 | reproduction rate | EC50 | 21 | days | >100 | mg/L | ○ | 4 OECD SIDS (HPVC) | Environment Agency of Japan | 1995 | 2017/02/06 | |||||||
甲殻類 | Daphnia magna | NOEC | 21 | days | >91 | 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 | reproduction rate | NOEC | 21 | days | >100 | mg/L | ○ | 4 OECD SIDS (HPVC) | Environment Agency of Japan | 1995 | 2017/02/06 | |||||||
甲殻類 | Daphnia magna | mortality | LC50 | 21 | days | >100 | mg/L | the pH was non-neutralized | ○ | 12 ECHA Information on Registered Substances | 1 | published report | 1997 | 2017/02/27 | |||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | >100 | mg/L | the pH was non-neutralized | ○ | 12 ECHA Information on Registered Substances | 1 | published report | 1997 | 2017/02/27 | |||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 0.72 | hours | 960000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2017/03/15 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 0.63 | hours | 1440000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2017/03/15 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 3.02 | hours | 480000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2017/03/15 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 1 | hours | 720000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2017/03/15 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 0.65 | hours | 1200000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2017/03/15 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 1.5 | hours | 600000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2017/03/15 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >720 | μmol/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hodson,P.V., D.G. Dixon, and K.L.E. Kaiser | Measurement of Median Lethal Dose as a Rapid Indication of Contaminant Toxicity to Fish | Environ. Toxicol. Chem.3(2): 243-254 | 1984 | 2017/03/15 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 3.02 | hours | 480000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2016/03/25 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | >720 | μmol/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hodson,P.V., D.G. Dixon, and K.L.E. Kaiser | Measurement of Median Lethal Dose as a Rapid Indication of Contaminant Toxicity to Fish | Environ. Toxicol. Chem.3(2): 243-254 | 1984 | 2016/03/25 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 0.63 | hours | 1440000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2016/03/25 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 1 | hours | 720000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2016/03/25 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 1.5 | hours | 600000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2016/03/25 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 0.65 | hours | 1200000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2016/03/25 | ||||||
魚類 | Carassius auratus (Goldfish) | Mortality | LT50 | 0.72 | hours | 960000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gersdorff,W.A. | Effect of Introducing the Carboxyl Group into the Phenol Molecule on Toxicity to Goldfish | Am. J. Pharm.:159-167 | 1943 | 2016/03/25 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LD50 | 4 | days | 1.01 | mmol/kg | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hodson,P.V., D.G. Dixon, and K.L.E. Kaiser | Measurement of Median Lethal Dose as a Rapid Indication of Contaminant Toxicity to Fish | Environ. Toxicol. Chem.3(2): 243-254 | 1984 | 2016/03/25 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Biochemical | 100~300 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pedersen,K.L., S.N. Pedersen, L.B. Christiansen, B. Korsgaard, and P. Bjerregaard | The Preservatives Ethyl-,Propyl-and Butylparaben are Oestrogenic in an In Vivo Fish Assay | Pharmacol. Toxicol.86:110-113 | 2000 | 2016/03/25 | ||||||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | 92.8 | mg/L | without pH adjustment, pH = 4.0 to 4.5 | ○ | 12 ECHA Information on Registered Substances | 1 | published study report | 1997 | 2017/02/28 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | >99.4 | mg/L | 12 ECHA Information on Registered Substances | 4 | Hodson PV, Dixon DG, Kaiser KLE | Measurement of median lethal dose as a rapid indication of contaminant toxicity | Environmental Toxicology and Chemistry | 1984 | 2017/02/27 | |||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 14 | days | 67 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | (Ⅱ-1)生態影響試験(藻類、甲殻類、魚類)結果一覧(平成28年3月版) | 2016 | 2016/11/08 | ||||||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 93 | 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 | Poecilia reticulata (Guppy) | LC50 | 14 | days | 66.5 | mg/L | ○ | 4 OECD SIDS (HPVC) | Environment Agency of Japan | 1995 | 2017/02/06 | ||||||||
魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 92.8 | mg/L | ○ | 4 OECD SIDS (HPVC) | Environment Agency of Japan | 1995 | 2017/02/06 | ||||||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | >100 | mg/L | with pH adjustment to pH = 6.7 | ○ | 12 ECHA Information on Registered Substances | 1 | published study report | 1997 | 2017/02/27 | |||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 14 | days | >100 | mg/L | test with pH adjustment (neutralisation) | ○ | 12 ECHA Information on Registered Substances | 1 | published study report | 1997 | 2017/02/27 | |||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 14 | days | 66.5 | mg/L | test with pH adjustment (neutralisation) | ○ | 12 ECHA Information on Registered Substances | 1 | published study report | 1997 | 2017/02/27 | |||||
魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 7 | days | 69.9 | mg/L | test without pH adjustment | ○ | 12 ECHA Information on Registered Substances | 1 | published study report | 1997 | 2017/02/27 | |||||
魚類 | Oryzias latipes (Japanese medaka) | NOEC | 14 | days | 31 | 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 |