【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 | LOEC | 7 | days | 4000 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 7 | days | 400 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | LOEC | 7 | days | 1000 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | |||||
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 | Pseudokirchneriella subcapitata | Population | 40~400 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Warshawsky,D., T. Cody, M. Radike, R. Reilman, B. Schumann, K. LaDow, and J. Schneider | Biotransformation of Benzo(a)pyrene and Other Polycyclic Aromatic Hydrocarbons and Hetercyclic Analogs by Several Green Algae and Other Algal Species | Chem.-Biol. Interact.97(2): 131-148 | 1995 | 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 | Dunaliella tertiolecta | Population | EC50 | 1 | hours | 23750 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | McFeters,G.A., P.J. Bond, S.B. Olson, and Y.T. Tchan | A Comparison of Microbial Bioassays for the Detection of Aquatic Toxicants | Water Res.17(12): 1757-1762 | 1983 | 2018/03/15 | |||||
藻類 | Desmodesmus sp. Desmodesmus armatus | Population | EC50 | 2 | days | 14 | μM | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bahrs,H., A. Putschew, and C.E.W. Steinberg | Toxicity of Hydroquinone to Different Freshwater Phototrophs is Influenced by Time of Exposure and pH | Environ. Sci. Pollut. Res.20(1): 146-154 | 2013 | 2018/03/15 | |||||
藻類 | Dunaliella tertiolecta | Population | EC50 | 1 | days | 29250 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | McFeters,G.A., P.J. Bond, S.B. Olson, and Y.T. Tchan | A Comparison of Microbial Bioassays for the Detection of Aquatic Toxicants | Water Res.17(12): 1757-1762 | 1983 | 2018/03/15 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 2 | days | 81 | μM | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bahrs,H., A. Putschew, and C.E.W. Steinberg | Toxicity of Hydroquinone to Different Freshwater Phototrophs is Influenced by Time of Exposure and pH | Environ. Sci. Pollut. Res.20(1): 146-154 | 2013 | 2018/03/15 | |||||
藻類 | Desmodesmus sp. Desmodesmus armatus | Population | EC50 | 4 | days | 17 | μM | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bahrs,H., A. Putschew, and C.E.W. Steinberg | Toxicity of Hydroquinone to Different Freshwater Phototrophs is Influenced by Time of Exposure and pH | Environ. Sci. Pollut. Res.20(1): 146-154 | 2013 | 2018/03/15 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | EC50 | 4 | days | 98 | μM | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bahrs,H., A. Putschew, and C.E.W. Steinberg | Toxicity of Hydroquinone to Different Freshwater Phototrophs is Influenced by Time of Exposure and pH | Environ. Sci. Pollut. Res.20(1): 146-154 | 2013 | 2018/03/15 | |||||
藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 0.33 | hours | 0.0005 | mol/dm3 FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andreozzi,R., M.S. Lo Casale, R. Marotta, G. Pinto, and A. Pollio | N-Methyl-P-Aminophenol (Metol) Ozonation in Aqueous Solution: Kinetics, Mechanism and Toxicological Characterization of Ozonized Samples | Water Res.34(18): 4419-4429 | 2000 | 2018/03/15 | ||||||
藻類 | Pseudokirchneriella subcapitata | Population | NOEC | 7 | days | 100 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | |||||
藻類 | Selenastrum capricornutum | 生長阻害 | EC50 | 7 | days | 1~4 | 11 Japan チャレンジプログラム | - | Environmental Effects of Photoprocessing Chemicals | National Association of Photographic Manufacturers, Inc. | 1974 | 2016/03/09 | |||||||
藻類 | Pseudokirchneriella subcapitata | cell number | EC50 | 72 | hours | 0.335 | mg/L | 12 ECHA Information on Registered Substances | 4 | Devillers J, Boule P, Vasseur P, Prevot P, Steiman R, Seigle-Murandi F, Beno t-Guyod JL, Nendza M, Gr oni C, Dive D, Chambon P | Environmental and health risks of hydroquinone. | Ecotoxicol Environ Saf | 1990 | 2016/02/17 | |||||
藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 0.053 | 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29年3月版) | 2018/02/19 | |||||||||
藻類 | Chlorella sp. Chlorella emersonii | slight activation of growth | 24 | hours | 10 | mg/L | 10 EHC (Environmental Health Criteria) | Devillers J, Boule P, Vasseur P, Prevot P, Steiman R, Seigle-Murandi F, Benoit-Guyod JL, Nendza M, Grioni C, Dive D, & Chambon P | Environmental and health risks of hydroquinone. | Ecotoxicol Environ Saf | 1990 | 2016/03/04 | |||||||
藻類 | Selenastrum capricornutum | growth | EC50 | 3 | days | 0.335 | mg/L | 10 EHC (Environmental Health Criteria) | Devillers J, Boule P, Vasseur P, Prevot P, Steiman R, Seigle-Murandi F, Benoit-Guyod JL, Nendza M, Grioni C, Dive D, & Chambon P | Environmental and health risks of hydroquinone. | Ecotoxicol Environ Saf | 1990 | 2018/03/13 | ||||||
藻類 | Selenastrum capricornutum | 増殖阻害 | EC50 | 72 | hours | 0.335 | mg/L | 18 既存化学物質安全性(ハザード)評価シート | EU | IUCLID(International Uniform Chemical Information Data Base) Data Sheet | 1995 | 2016/02/23 | |||||||
藻類 | Scenedesmus sp. Scenedesmus quadricauda | toxicity threshold concentration for inhibition of cell multiplication | 7 | days | 0.93 | mg/L | 10 EHC (Environmental Health Criteria) | Bringmann G | Determination of the biological harmful effect of water pollutants on protozoa. I. Bacteriophagic flagellates (model organism: Entosiphon sulcatum Stein). | Z Wasser Abwasser-Forsch | 1978 | 2016/03/04 | |||||||
藻類 | Scenedesmus sp. Scenedesmus quadricauda | toxicity threshold concentration for inhibition of cell multiplication | 96 | hours | 4 | mg/L | 10 EHC (Environmental Health Criteria) | Bringmann G & Kühn R | Comparative water toxicology studies on bacteria, algae and small crustaceans. | Gesundheits-Ingenieur | 1959 | 2016/03/04 | |||||||
藻類 | Pseudokirchneriella subcapitata | yield | EC50 | 72 | hours | <0.033 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Pseudokirchneriella subcapitata | 生長阻害 | NOErC | 72 | hours | 0.0015 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.053 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Pseudokirchneriella subcapitata | yield | EC50 | 72 | hours | 0.041 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Chlorella sp. Chlorella pyrenoidosa | Population | EC50 | 80 | hours | 11000 | 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 | Dedonder, A., and C.F. Van Sumere | The Effect of Phenolics and Related Compounds on the Growth and the Respiration of Chlorella vulgaris. | Z.Pflanzenphysiol. (U.S.EPA「AQUIRE」) | 1971 | 2018/03/17 | |||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | EC50 | 3 | days | 53 | 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 | 環境省 | 平成19 年度生態影響試験 | 2008 | 2018/03/17 | ||||||
藻類 | Selenastrum capricornutum | 生長阻害 | EC50 | 72 | hours | 0.335 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Devillers et al. | Environmental and Health Risks of Hydropuinone | Ecotoxicology and Environmental safety | 1990 | 2018/03/17 | ||||||
藻類 | Pseudokirchneriella subcapitata | Growth | EC50 | 3 | days | 335 | 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) | D | Devillers, J., P. Boule, P. Vasseur, P. Prevot, R. Steiman, F. Seigle-Murandi, J. L. Benoit-Guyod, M. Nendza, C. Grioni, D.Dive, and P. Chambon | Environmental and Health Risks of Hydroquinone. | Ecotoxicol.Environ.Saf. | 1990 | 2018/03/05 | |||||
藻類 | Selenastrum sp. S. quadricauda | EC50 | 7 | days | 0.93 | mg/L | 4 OECD SIDS (HPVC) | U.S. Environmental Protection Agency, | Pre-SIAR meeting comments. | 1995 | 2018/03/10 | ||||||||
藻類 | Selenastrum sp. S. quadricauda | EC50 | 96 | hours | 4 | mg/L | 4 OECD SIDS (HPVC) | U.S. Environmental Protection Agency, | Pre-SIAR meeting comments. | 1995 | 2018/03/10 | ||||||||
藻類 | Selenastrum capricornutum | EC50 | 72 | hours | 0.335 | mg/L | 4 OECD SIDS (HPVC) | U.S. Environmental Protection Agency, | Pre-SIAR meeting comments. | 1995 | 2018/03/10 | ||||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.33 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Pseudokirchneriella subcapitata | 生長阻害 | ErC50 | 72 | hours | 0.053 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
藻類 | Selenastrum capricornutum | growth inhibition | EC50 | 7 | days | 1~4 | × | 4 OECD SIDS (HPVC) | National Association of Photographic Manufacturers, Inc. | Environmental Effects of Photoprocessing Chemicals | 1974 | 2018/03/10 | |||||||
藻類 | Selenastrum capricornutum | EC50 | 72 | hours | 1~4 | × | 4 OECD SIDS (HPVC) | National Association of Photographic Manufacturers, Inc | Environmental Effects of Photoprocessing Chemicals | 1974 | 2016/02/19 | ||||||||
藻類 | Selenastrum capricornutum | 生長阻害 | NOEC | 7 | days | 0.4 | mg/L | 11 Japan チャレンジプログラム | - | Environmental Effects of Photoprocessing Chemicals | National Association of Photographic Manufacturers, Inc. | 1974 | 2016/03/09 | ||||||
藻類 | Selenastrum capricornutum | 生長阻害 | LOEC | 7 | days | 1 | mg/L | 11 Japan チャレンジプログラム | - | Environmental Effects of Photoprocessing Chemicals | National Association of Photographic Manufacturers, Inc. | 1974 | 2016/03/27 | ||||||
藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 0.0015 | 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29年3月版) | 2018/02/19 | |||||||||
藻類 | Chlorella sp. Chlorella emersonii | lowest concentration for no detectable growth | LOEC | 14 | days | 79.4 | mg/L | 10 EHC (Environmental Health Criteria) | Wängberg SA & Blanck H | Multivariate patterns of algal sensitivity to chemicals in relation to phylogeny. | Ecotoxicol Environ Saf | 1988 | 2018/03/14 | ||||||
藻類 | Scenedesmus sp. Scenedesmus obtusiusculus | lowest concentration for no detectable growth | LOEC | 14 | days | 39.8 | mg/L | 10 EHC (Environmental Health Criteria) | Wängberg SA & Blanck H | Multivariate patterns of algal sensitivity to chemicals in relation to phylogeny. | Ecotoxicol Environ Saf | 1988 | 2018/03/13 | ||||||
藻類 | Selenastrum capricornutum | lowest concentration for nodetectable growth | LOEC | 14 | days | 79.4 | mg/L | 10 EHC (Environmental Health Criteria) | Wängberg SA & Blanck H | Multivariate patterns of algal sensitivity to chemicals in relation to phylogeny. | Ecotoxicol Environ Saf | 1988 | 2018/03/13 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 0.019 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | EC10 | 72 | hours | 0.034 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Pseudokirchneriella subcapitata | yield | EC10 | 72 | hours | 0.009 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 0.002 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Pseudokirchneriella subcapitata | yield | NOEC | 72 | hours | 0.009 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Scenedesmus sp. Scenedesmus quadriccauda | 生長阻害 | EC3 | 8 | days | 0.93 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Bringmann, G. and Kuhn, R. | Befunde der Schadwirkung wassergefahrdender Stoffe gegen Bakterien Daphinia magna | Z. Wasser Abwasser Forsch. | 1977 | 2018/03/18 | ||||||
藻類 | Pseudokirchneriella subcapitata | Growth rate | NOEC | 3 | days | 1.5 | 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 | 環境省 | 平成19 年度生態影響試験 | 2008 | 2018/03/17 | ||||||
藻類 | Pseudokirchneriella subcapitata | yield | NOEC | 72 | hours | <0.033 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
藻類 | Anabaena sp. | lowest concentration for no detectable growth | LOEC | 14 | days | 10 | mg/L | 10 EHC (Environmental Health Criteria) | Wängberg SA & Blanck H | Multivariate patterns of algal sensitivity to chemicals in relation to phylogeny. | Ecotoxicol Environ Saf | 1988 | 2018/03/14 | ||||||
藻類 | Anabaena flos-aquae | lowest concentration for no detectable growth | LOEC | 14 | days | 39.8 | mg/L | 10 EHC (Environmental Health Criteria) | Wängberg SA & Blanck H | Multivariate patterns of algal sensitivity to chemicals in relation to phylogeny. | Ecotoxicol Environ Saf | 1988 | 2018/03/14 | ||||||
藻類 | Selenastrum capricornutum | growth inhibition | NOEC | 7 | days | 0.4 | mg/L | × | 4 OECD SIDS (HPVC) | National Association of Photographic Manufacturers, Inc. | Environmental Effects of Photoprocessing Chemicals | 1974 | 2018/03/10 | ||||||
甲殻類 | Daphnia magna | Behavior | EC100 | 1 | days | 190 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bringmann,G., and R. Kuehn | Results of Toxic Action of Water Pollutants on Daphnia magna Straus Tested by an Improved Standardized Procedure | Z. Wasser-Abwasser-Forsch.15(1): 1-6 | 1982 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 0.25 | days | <1000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Devillers,J., T. Meunier, and P. Chambon | Usefulness of the Dosage-Effect-Time Relation in Ecotoxicology for the Determination of Different Chemical Classes of Toxicants (Interet de la Relation Dose-Effet-Temps en Ecotoxicologie pour la Determination des Differe | Tech. Sci. Munic.80:329-334 | 1985 | 2018/03/15 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 1 | days | 150 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Crisinel,A., L. Delaunay, D. Rossel, J. Tarradellas, H. Meyer, H. Saiah, P. Vogel, C. Delisle, and C. Blaise | Cyst-Based Ecotoxicological Tests Using Anostracans: Comparison of Two Species of Streptocephalus | Environ. Toxicol. Water Qual.9(4): 317-326 | 1994 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Mortality | 4 | days | 91 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | ||||||
甲殻類 | Daphnia magna | Intoxication | LC0 | 1 | days | 40 | μg/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:26 p. | 1977 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 1 | days | 320 | μg/L | FORMULATION | 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 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Behavior | EC50 | 1 | days | 120 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bringmann,G., and R. Kuehn | Results of Toxic Action of Water Pollutants on Daphnia magna Straus Tested by an Improved Standardized Procedure | Z. Wasser-Abwasser-Forsch.15(1): 1-6 | 1982 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 2 | days | 130 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Crisinel,A., L. Delaunay, D. Rossel, J. Tarradellas, H. Meyer, H. Saiah, P. Vogel, C. Delisle, and C. Blaise | Cyst-Based Ecotoxicological Tests Using Anostracans: Comparison of Two Species of Streptocephalus | Environ. Toxicol. Water Qual.9(4): 317-326 | 1994 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Intoxication | LC100 | 1 | days | 310 | μg/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:26 p. | 1977 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Mortality | 3 | days | 300 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/15 | ||||||
甲殻類 | Daphnia magna | Intoxication | LC50 | 1 | days | 90 | μg/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:26 p. | 1977 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 2 | days | 290 | μg/L | FORMULATION | 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 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Mortality | LC50 | 4 | days | 50 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Mortality | LC50 | 4 | days | >90 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Physiology | 1 | days | 50~500 | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Kolupayev,Y.I. | Sensitivity of Test Functions as a Basis for Selecting Bioassays for Aquatic Toxicity | Hydrobiol. J.25(5): 52-54 | 1990 | 2016/03/25 | ||||||||
甲殻類 | Daphnia magna | Behavior | 2 | days | 600 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bringmann,G., and R. Kuhn | Comparative Water-Toxicological Investigations on Bacteria, Algae, and Daphnia | TR-TS-002, Literature Research Company, Annandale, VA:26 p. | 1959 | 2016/03/25 | |||||||
甲殻類 | Daphnia sp. | Mortality | LD50 | 2 | days | 400000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bringmann,G., and R. Kuhn | The Water-Toxicological Detection of Insecticides (Zum Wasser-Toxikologischen Nachweis von Insektiziden) | Gesund. -Ing.8:243-244 | 1960 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 2 | hours | 10000~35000 | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Devillers,J., T. Meunier, and P. Chambon | Usefulness of the Dosage-Effect-Time Relation in Ecotoxicology for the Determination of Different Chemical Classes of Toxicants (Interet de la Relation Dose-Effet-Temps en Ecotoxicologie pour la Determination des Differe | Tech. Sci. Munic.80:329-334 | 1985 | 2016/03/25 | ||||||
甲殻類 | Daphnia magna | Physiology | EC50 | 4 | hours | 3500~10000 | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Devillers,J., T. Meunier, and P. Chambon | Usefulness of the Dosage-Effect-Time Relation in Ecotoxicology for the Determination of Different Chemical Classes of Toxicants (Interet de la Relation Dose-Effet-Temps en Ecotoxicologie pour la Determination des Differe | Tech. Sci. Munic.80:329-334 | 1985 | 2016/03/25 | ||||||
甲殻類 | Daphnia sp. Daphnia pulicaria | Mortality | LC50 | 2 | days | 162 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | DeGraeve,G.M., D.L. Geiger, J.S. Meyer, and H.L. Bergman | Acute and Embryo-Larval Toxicity of Phenolic Compounds to Aquatic Biota | Arch. Environ. Contam. Toxicol.9(5): 557-568 | 1980 | 2018/03/15 | |||||
甲殻類 | Daphnia magna | Behavior | EC0 | 1 | days | 50 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bringmann,G., and R. Kuehn | Results of Toxic Action of Water Pollutants on Daphnia magna Straus Tested by an Improved Standardized Procedure | Z. Wasser-Abwasser-Forsch.15(1): 1-6 | 1982 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | Intoxication | EC50 | 1 | days | <1000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Devillers,J., T. Meunier, and P. Chambon | Usefulness of the Dosage-Effect-Time Relation in Ecotoxicology for the Determination of Different Chemical Classes of Toxicants (Interet de la Relation Dose-Effet-Temps en Ecotoxicologie pour la Determination des Differe | Tech. Sci. Munic.80:329-334 | 1985 | 2018/03/09 | |||||
甲殻類 | Daphnia magna | mobility | LC0 | 24 | hours | 0.04 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | Bringmann G, Kühn R | Befunde der Schadwirkung wassergefährdender Stoffe gegen Daphnia magna. | Z Wasser AbwasserForschung | 1977 | 2016/02/16 | ||||
甲殻類 | Daphnia magna | mobility | LC100 | 24 | hours | 0.31 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | Bringmann G, Kühn R | Befunde der Schadwirkung wassergefährdender Stoffe gegen Daphnia magna. | Z Wasser AbwasserForschung | 1977 | 2016/02/16 | ||||
甲殻類 | Daphnia magna | mobility | LC50 | 24 | hours | 0.09 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | Bringmann G, Kühn R | Befunde der Schadwirkung wassergefährdender Stoffe gegen Daphnia magna. | Z Wasser AbwasserForschung | 1977 | 2016/02/16 | ||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.29 | mg/L | 12 ECHA Information on Registered Substances | 2 | Kühn R, Pattard M, Pernak KD, Winter A | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna. | Water Res | 1989 | 2016/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC100 | 48 | hours | 0.71 | mg/L | 12 ECHA Information on Registered Substances | 2 | Kühn R, Pattard M, Pernak KD, Winter A | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna. | Water Res | 1989 | 2016/02/16 | |||||
甲殻類 | Daphnia magna | mobility | EC0 | 48 | hours | 0.13 | mg/L | 12 ECHA Information on Registered Substances | 2 | Kühn R, Pattard M, Pernak KD, Winter A | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna. | Water Res | 1989 | 2016/02/16 | |||||
甲殻類 | Daphnia magna | 遊泳阻害 | 96 | hours | 0.05 | mg/L | × | 11 Japan チャレンジプログラム | - | Environmental Effects of Photoprocessing Chemicals | National Association of Photographic Manufacturers, Inc. | 1974 | 2016/03/09 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.13 | mg/L | 12 ECHA Information on Registered Substances | 2 | Crisinel A, Delaunay L, Rossel D, Tarradellas J, Meyer H, Saiah H, Vogel P, Delisle C, Blaise C | Cystbased ecotox cological tests using Anostracans: Comparison of two species of Streptocephalus. | Environ Toxicol Water Qual | 1994 | 2016/02/16 | |||||
甲殻類 | Daphnia magna | EC50 | 48 | hours | 0.061 | 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29年3月版) | 2018/02/19 | |||||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC0 | 48 | hours | 0.13 | mg/L | 10 EHC (Environmental Health Criteria) | Kühn R, Pattard M, Pernak K-D, & Winter A | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna. | Water Res | 1989 | 2016/03/04 | ||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC50 | 24 | hours | 0.137 | mg/L | 10 EHC (Environmental Health Criteria) | Devillers J, Chambon P, Zakarya D, Chastrette M, & Chambon R | A predictive structure-toxicity model with Daphnia magna. | Chemosphere | 1987 | 2018/03/13 | ||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC50 | 24 | hours | 0.12 | mg/L | 10 EHC (Environmental Health Criteria) | Bringmann G & Kühn R | Findings concerning the harmful effect of water pollutants on Daphnia magna in an advanced standardized test procedure. | Z Wasser Abwasser Forsch | 1982 | 2018/03/13 | ||||||
甲殻類 | Daphnia magna | LC100 | 24 | hours | 0.31 | mg/L | 10 EHC (Environmental Health Criteria) | Bringmann G & Kühn R | Findings concerning the harmful effect of water pollutants on Daphnia magna. | Z Wasser Abwasser Forsch | 1977 | 2018/03/13 | |||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC50 | 48 | hours | 0.29 | mg/L | 10 EHC (Environmental Health Criteria) | Kühn R, Pattard M, Pernak K-D, & Winter A | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna. | Water Res | 1989 | 2016/03/04 | ||||||
甲殻類 | Daphnia sp. Daphnia pulicaria | LC50 | 48 | hours | 0.162 | mg/L | 10 EHC (Environmental Health Criteria) | DeGraeve GM, Geiger DL, Meyer JS, & Bergman HL | Acute and embryo-larval toxicity of phenolic compounds to aquati biota. | Environ Contam Toxicol | 1980 | 2016/03/04 | |||||||
甲殻類 | Daphnia magna | toxicity threshold concentration for inhibition of mobility | 48 | hours | 0.6 | mg/L | 10 EHC (Environmental Health Criteria) | Bringmann G & Kühn R | Comparison of the effect of harmful substances on flagellates and ciliates with the effect of holozoic bacteriophagic and saprozoic protozoa. | GWF-Wasser/Abwasser | 1981 | 2016/03/04 | |||||||
甲殻類 | Daphnia magna | LC50 | 24 | hours | 0.09 | mg/L | 10 EHC (Environmental Health Criteria) | Bringmann G & Kühn R | Findings concerning the harmful effect of water pollutants on Daphnia magna. | Z Wasser Abwasser Forsch | 1977 | 2018/03/13 | |||||||
甲殻類 | Daphnia sp. Daphnia pulex | LC100 | 0.1 | hours | 8809 | mg/L | 10 EHC (Environmental Health Criteria) | Stom DJ, Geel TA, & Balayan AE | Effect of individual phenolic compounds and their mixtures on luminous bacteria. Part I: Use of bacterial luminescence extinguishing for biotesting of phenols. | Acta Hydrochim Hydrobiol | 1986 | 2016/03/04 | |||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC50 | 24 | hours | 0.15 | mg/L | 10 EHC (Environmental Health Criteria) | Tissot A, Boule P, Lemaire J, Lambert S, & Palla JC | Photochimie et environnement. X. Evaluation de la toxicité des produits de phototransformation de l'hydroquinone et des chlorophénols en milieu aqueux. | Chemosphere | 1985 | 2016/03/04 | ||||||
甲殻類 | Daphnia magna | LC0 | 24 | hours | 0.04 | mg/L | 10 EHC (Environmental Health Criteria) | Bringmann G & Kühn R | Findings concerning the harmful effect of water pollutants on Daphnia magna. | Z Wasser Abwasser Forsch | 1977 | 2018/03/13 | |||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC100 | 48 | hours | 0.71 | mg/L | 10 EHC (Environmental Health Criteria) | Kühn R, Pattard M, Pernak K-D, & Winter A | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna. | Water Res | 1989 | 2016/03/04 | ||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC0 | 24 | hours | 0.05 | mg/L | 10 EHC (Environmental Health Criteria) | Bringmann G & Kühn R | Findings concerning the harmful effect of water pollutants on Daphnia magna in an advanced standardized test procedure. | Z Wasser Abwasser Forsch | 1982 | 2018/03/13 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 48 | hours | 0.13 | mg/L | 18 既存化学物質安全性(ハザード)評価シート | US EPA | AQUIRE(ECOTOX Database System) | 2016/02/23 | ||||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC0 | 24 | hours | 0.13 | mg/L | 10 EHC (Environmental Health Criteria) | Kühn R, Pattard M, Pernak K-D, & Winter A | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna. | Water Res | 1989 | 2018/03/13 | ||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC100 | 24 | hours | 0.71 | mg/L | 10 EHC (Environmental Health Criteria) | Kühn R, Pattard M, Pernak K-D, & Winter A | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna. | Water Res | 1989 | 2016/03/04 | ||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC100 | 24 | hours | 0.19 | mg/L | 10 EHC (Environmental Health Criteria) | Bringmann G & Kühn R | Findings concerning the harmful effect of water pollutants on Daphnia magna in an advanced standardized test procedure. | Z Wasser Abwasser Forsch | 1982 | 2018/03/13 | ||||||
甲殻類 | Daphnia magna | inhibition of mobility | EC50 | 24 | hours | 0.32 | mg/L | 10 EHC (Environmental Health Criteria) | Kühn R, Pattard M, Pernak K-D, & Winter A | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna. | Water Res | 1989 | 2018/03/13 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 48 | hours | 0.061 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.061 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | mobility | NOEC | 24 | hours | 0.095 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 0.148 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC0 | 48 | hours | 0.029 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
甲殻類 | Daphnia magna | mobility | EC100 | 24 | hours | 0.11 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | mobility | EC100 | 48 | hours | 0.11 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC100 | 24 | hours | 0.11 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC0 | 24 | hours | 0.029 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 24 | hours | 0.071 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
甲殻類 | Daphnia magna | mobility | NOEC | 48 | hours | 0.029 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 24 | hours | 0.071 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | mobility | NOEC | 24 | hours | 0.029 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 2 | hours | 10~35 | 8 NITE 化学物質の初期リスク評価書 | Devillers, J., Meunier, T. and Chambon, P. | Advantage of the dosage-action-time relation in ecotoxicology for the test of the various chemical species of toxics | Tech. Sci.Munic. | 1985 | 2018/03/18 | |||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 24 | hours | <1 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Devillers, J., Meunier, T. and Chambon, P. | Advantage of the dosage-action-time relation in ecotoxicology for the test of the various chemical species of toxics | Tech. Sci.Munic. | 1985 | 2018/03/18 | ||||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 2 | days | 290 | 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 | Kühn, R., M. Pattard, K. Pernak, and A. Winter | Results of the Harmful Effects of Selected Water Pollutants (Anilines, Phenols, Aliphatic Compounds) to Daphnia magna. | Water Res. (U.S.EPA「AQUIRE」) | 1989 | 2018/03/17 | |||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 48 | hours | 0.29 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Kuhn, R., Pattard, M.Pernak, K. and Winter, A. | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna | Water Res. | 1989 | 2018/03/22 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 24 | hours | 0.137 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Devillers, J., Chambon, P. and Zakarya, D. | A predictive structure-toxicitymodel with Daphnia magna. | Chemosphere | 1987 | 2018/03/22 | ||||||
甲殻類 | Daphnia sp. Daphnia pulicaria | Mortality | LC50 | 2 | days | 162 | 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 | DeGraeve, G.M., D.L. Geiger, J.S. Meyer, and H.L. Bergman | Acute and Embryo-Larval Toxicity of Phenolic Compounds to Aquatic Biota. | Arch. Environ. Contam. Toxicol. (U.S.EPA「AQUIRE」) | 1980 | 2018/03/17 | |||||
甲殻類 | Daphnia magna | LC50 | 24 | hours | 0.09 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Bringmann, G. and Kuhn, R. | Befunde der Schadwirkung wassergefahrdender stoffe gegen Bakterien Daphnia magna | Z. Wasser Abwasser Forsch. | 1977 | 2018/03/18 | |||||||
甲殻類 | Daphnia sp. Daphnia pulicaria | LC50 | 48 | hours | 0.162 | mg/L | 8 NITE 化学物質の初期リスク評価書 | DeGraeve, G.M., Geiger, D.L., Meyer, J.S. and Bergman, H.L. | Acute and embryo-larval toxicity of phenolic compounds aquatic biota. | Arch. Environ. Contam. Toxicol. | 1980 | 2018/03/18 | |||||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 2 | days | 61 | 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 | 環境省 | 平成19 年度生態影響試験 | 2008 | 2018/03/05 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 24 | hours | 0.15 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Crisinel, A., Delaunay, L., Rossel, D., Tarradellas, J., Meer, H., Saiah, H., Vogel, P., Delisle, C. And Blaise, C. | Cyst-based ecotoxicological tests using anostracans: comparison of two species of streptocephalus | Environ. Toxicol.Water Qual. | 1994 | 2018/03/18 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 24 | hours | 0.32 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Kuhn, R., Pattard, M.Pernak, K. and Winter, A. | Results of the harmful effects of selected water pollutants (anilines, phenols, aliphatic compounds) to Daphnia magna | Water Res. | 1989 | 2018/03/22 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 4 | hours | 3.5~10 | 8 NITE 化学物質の初期リスク評価書 | Devillers, J., Meunier, T. and Chambon, P. | Advantage of the dosage-action-time relation in ecotoxicology for the test of the various chemical species of toxics | Tech. Sci.Munic. | 1985 | 2018/03/18 | |||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 48 | hours | 0.13 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Crisinel, A., Delaunay, L., Rossel, D., Tarradellas, J., Meer, H., Saiah, H., Vogel, P., Delisle, C. And Blaise, C. | Cyst-based ecotoxicological tests using anostracans: comparison of two species of streptocephalus | Environ. Toxicol.Water Qual. | 1994 | 2018/03/18 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 24 | hours | 0.12 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Bringann, G. and Kuhn, R. | Ergebnisse der Schadwirkung wassergefahrdender Stoffe genen Daphnia magna in Einem Weiterentwickelten Standardisierten Testverfahren. | Z.Wasser Abwaser Forsch. | 1982 | 2018/03/18 | ||||||
甲殻類 | Daphnia magna | Immobilization | EC50 | 2 | days | 130 | 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 | Crisinel, A., L. Delaunay, D. Rossel, J. Tarradellas, H. Meyer, H. Saiah, P. Vogel, C. Delisle, and C. Blaise | Cyst-Based Ecotoxicological Tests Using Anostracans: Comparison of Two Species of Streptocephalus. | Environ.Toxicol.Water Qual. (U.S.EPA「AQUIRE」) | 1994 | 2018/03/17 | |||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 6 | hours | <1 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Devillers, J., Meunier, T. and Chambon, P. | Advantage of the dosage-action-time relation in ecotoxicology for the test of the various chemical species of toxics | Tech. Sci.Munic. | 1985 | 2018/03/18 | ||||||
甲殻類 | Daphnia magna | LC50 | 24 | hours | 0.12 | mg/L | × | 4 OECD SIDS (HPVC) | Bringmann, G., and Kühn, R. | Results of Toxic Action of Water Pollutants on Daphnia magna (Straus) Tested by an Improved Standardized Procedure | Z. Wasser Abwasser Forsch. | 1982 | 2018/03/10 | ||||||
甲殻類 | Daphnia magna | LC50 | 24 | hours | 0.09 | mg/L | × | 4 OECD SIDS (HPVC) | Bringmann, G., and Kühn, R. | Results of the Damaging Effect of Water Pollutants on Daphnia magna | Z. Wasser Abwasser Forsch. | 1974 | 2018/03/10 | ||||||
甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.134 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC100 | 48 | hours | 0.11 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 24 | hours | 0.11 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Rhone poulenc | (EU, 2000から引用) | 1977 | 2018/03/22 | |||||||
甲殻類 | Daphnia magna | immobilization | LC50 | 48 | hours | 0.29 | mg/L | 4 OECD SIDS (HPVC) | Kühn, R., Pattard, M., Pernak, K-D., and Winter, A. | Results of the harmful effects of selected water pollutants (anilines, pheonls, aliphatic compounds) to Daphnia magna. | Wat. Res. | 1989 | 2018/03/10 | ||||||
甲殻類 | Daphnia magna | LC50 | 96 | hours | 0.05 | mg/L | × | 4 OECD SIDS (HPVC) | National Association of Photographic Manufacturers, Inc., | Environmental Effects of Photoprocessing Chemicals, | 1974 | 2018/03/10 | |||||||
甲殻類 | Daphnia magna | LC50 | 48 | hours | 0.05 | mg/L | × | 4 OECD SIDS (HPVC) | National Association of Photographic Manufacturers, Inc., | Brachydanio rerio and Leuciscus idus in the Study of the Toxicity to Fish of Chemical Compounds and Wastewaters | Environmental Effects of Photoprocessing Chemicals | 1974 | 2016/02/19 | ||||||
甲殻類 | Daphnia magna | EC50 | 24 | hours | 0.12 | mg/L | × | 4 OECD SIDS (HPVC) | Bringmann, G., and Kühn, R | Results of Toxic Action of Water Pollutants on Daphnia magna (Straus) Tested by an Improved Standardized Procedure Brachydanio rerio and Leuciscus idus in the Study of the Toxicity to Fish of Chemical Compounds and Wastewaters | Z. Wasser Abwasser Forsch | 1982 | 2016/02/18 | ||||||
甲殻類 | Daphnia magna | EC50 | 21 | days | 0.08 | 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29年3月版) | 2018/02/19 | |||||||||
甲殻類 | Daphnia magna | NOEC | 21 | days | 0.0029 | 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29年3月版) | 2018/02/19 | |||||||||
甲殻類 | Daphnia magna | body length of parent daphnids | NOEC | 21 | days | 0.054 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 0.003 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | first day of birth | NOEC | 21 | days | >0.076 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | body length of parent daphnids | NOEC | 21 | days | 0.039 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | reproduction | LOEC | 21 | days | 0.005 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | reproduction | NOEC | 21 | days | 0.006 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | body length of parent daphnias | LOEC | 21 | days | 0.076 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | 累積生存産仔数 | NOEC | 21 | days | 0.0029 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
甲殻類 | Daphnia magna | 累積生存産仔数 | LOEC | 21 | days | 0.0049 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
甲殻類 | Daphnia magna | 繁殖阻害 | EC50 | 21 | days | 0.08 | mg/L | 11 Japan チャレンジプログラム | 2018/03/17 | ||||||||||
甲殻類 | Daphnia magna | first day of birth | LOEC | 21 | days | 0.076 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | LC50 | 21 | days | 0.061 | mg/L | 11 Japan チャレンジプログラム | 2018/03/18 | |||||||||||
甲殻類 | Daphnia magna | Reproduction | NOEC | 21 | days | 2.9 | 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 | 環境省 | 平成19 年度生態影響試験 | 2008 | 2018/03/05 | ||||||
甲殻類 | Daphnia magna | mobility | NOEC | 48 | hours | 0.095 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | mortality | LC50 | 21 | days | 0.061 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
甲殻類 | Daphnia magna | reproduction | EC50 | 21 | days | 0.08 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2018/01/30 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | 1 | days | 1000 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC0 | 4 | days | <1000 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Buzzell,J.C.,Jr., R.H.F. Young, and D.W. Ryckman | Behavior of Organic Chemicals in the Aquatic Environment. Part II. - Behavior in Dilute Systems | Environ.Sanitary Engineering Labs., Washington University, St.Louis, MO:81 p. | 1968 | 2018/03/09 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | EC50 | 2 | days | 3200 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lahnsteiner,F. | The Sensitivity and Reproducibility of the Zebrafish (Danio rerio) Embryo Test for the Screening of Waste Water Quality and for Testing the Toxicity of Chemicals | Alt. Lab. Anim. (ATLA)36(3): 299-311 | 2008 | 2018/03/09 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 0.25 | days | <1000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Devillers,J., T. Meunier, and P. Chambon | Usefulness of the Dosage-Effect-Time Relation in Ecotoxicology for the Determination of Different Chemical Classes of Toxicants (Interet de la Relation Dose-Effet-Temps en Ecotoxicologie pour la Determination des Differe | Tech. Sci. Munic.80:329-334 | 1985 | 2018/03/15 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 5.8 | μmol/L | ACTIVE INGREDIENT | 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 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LT50 | 4 | days | 100 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Terhaar,C.J., W.S. Ewell, S.P. Dziuba, and D.W. Fassett | Toxicity of Photographic Processing Chemicals to Fish | Photogr. Sci. Eng.16(5): 370-377 | 1972 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | <100 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 4 | days | 170 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wellens,H. | Comparison of the Sensitivity of Brachydanio rerio and Leuciscus idus by Testing the Fish Toxicity of Chemicals and Wastewaters | Z. Wasser-Abwasser-Forsch.51(2): 49-52 | 1982 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | >130 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LT50 | 4 | days | 400 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Terhaar,C.J., W.S. Ewell, S.P. Dziuba, and D.W. Fassett | Toxicity of Photographic Processing Chemicals to Fish | Photogr. Sci. Eng.16(5): 370-377 | 1972 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | 4 | days | 100 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LT50 | 4 | days | 50 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Terhaar,C.J., W.S. Ewell, S.P. Dziuba, and D.W. Fassett | Toxicity of Photographic Processing Chemicals to Fish | Photogr. Sci. Eng.16(5): 370-377 | 1972 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | 4 | days | 100 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 97 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | DeGraeve,G.M., D.L. Geiger, J.S. Meyer, and H.L. Bergman | Acute and Embryo-Larval Toxicity of Phenolic Compounds to Aquatic Biota | Arch. Environ. Contam. Toxicol.9(5): 557-568 | 1980 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LT50 | 4 | days | 200 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Terhaar,C.J., W.S. Ewell, S.P. Dziuba, and D.W. Fassett | Toxicity of Photographic Processing Chemicals to Fish | Photogr. Sci. Eng.16(5): 370-377 | 1972 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | 1 | days | 180 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC0 | 2 | days | 100 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lysak,A., and J. Marcinek | Multiple Toxic Effect of Simultaneous Action of Some Chemical Substances on Fish | Rocz. Nauk Roln. Ser. H Rybactwo.94(3): 53-63 | 1972 | 2018/03/09 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 44 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | DeGraeve,G.M., D.L. Geiger, J.S. Meyer, and H.L. Bergman | Acute and Embryo-Larval Toxicity of Phenolic Compounds to Aquatic Biota | Arch. Environ. Contam. Toxicol.9(5): 557-568 | 1980 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LT50 | 0.46 | days | 200 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Terhaar,C.J., W.S. Ewell, S.P. Dziuba, and D.W. Fassett | Toxicity of Photographic Processing Chemicals to Fish | Photogr. Sci. Eng.16(5): 370-377 | 1972 | 2018/03/15 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC100 | 2 | days | >400 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lysak,A., and J. Marcinek | Multiple Toxic Effect of Simultaneous Action of Some Chemical Substances on Fish | Rocz. Nauk Roln. Ser. H Rybactwo.94(3): 53-63 | 1972 | 2018/03/09 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 1 | days | <1000 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Devillers,J., T. Meunier, and P. Chambon | Usefulness of the Dosage-Effect-Time Relation in Ecotoxicology for the Determination of Different Chemical Classes of Toxicants (Interet de la Relation Dose-Effet-Temps en Ecotoxicologie pour la Determination des Differe | Tech. Sci. Munic.80:329-334 | 1985 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 100~180 | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | National Association of Photographic Manufacturers | Environmental Effect of Photoprocessing Chemicals Vol I and II (557) | EPA/OTS Doc. #40-8469216:536 p. | 1974 | 2018/03/09 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | 0.92 | days | 200 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Terhaar,C.J., W.S. Ewell, S.P. Dziuba, and D.W. Fassett | Toxicity of Photographic Processing Chemicals to Fish | Photogr. Sci. Eng.16(5): 370-377 | 1972 | 2018/03/15 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LD50 | 4 | days | 0.22 | 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 | Cyprinus carpio (Carp) | Mortality | 1.92 | days | 144 | 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 | Carassius auratus (Goldfish) | Mortality | 2 | days | 287 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sollmann,T. | Correlation of the Aquarium Goldfish Toxicities of Some Phenols, Quinones, and Other Benzene Derivatives with Their Inhibition of Autooxidative | J. Gen. Physiol.32:671-679 | 1949 | 2016/03/25 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LD50 | 4 | days | 2.09 | mmol/kg | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hodson,P.V. | A Comparison of the Acute Toxicity of Chemicals to Fish, Rats and Mice | J. Appl. Toxicol.5(4): 220-226 | 1985 | 2016/03/25 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 4 | hours | 1000~3500 | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Devillers,J., T. Meunier, and P. Chambon | Usefulness of the Dosage-Effect-Time Relation in Ecotoxicology for the Determination of Different Chemical Classes of Toxicants (Interet de la Relation Dose-Effet-Temps en Ecotoxicologie pour la Determination des Differe | Tech. Sci. Munic.80:329-334 | 1985 | 2016/03/25 | ||||||
魚類 | Danio rerio (Zebrafish) | Mortality | LC50 | 2 | hours | 1000~3500 | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Devillers,J., T. Meunier, and P. Chambon | Usefulness of the Dosage-Effect-Time Relation in Ecotoxicology for the Determination of Different Chemical Classes of Toxicants (Interet de la Relation Dose-Effet-Temps en Ecotoxicologie pour la Determination des Differe | Tech. Sci. Munic.80:329-334 | 1985 | 2016/03/25 | ||||||
魚類 | Lepomis macrochirus (Bluegill) | No Group Code | 6 | hours | 5000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Applegate,V.C., J.H. Howell, A.E.,Jr. Hall, and M.A. Smith | Toxicity of 4,346 Chemicals to Larval Lampreys and Fishes | Spec.Sci.Rep.Fish.No.207, Fish Wildl.Serv., U.S.D.I., Washington, DC:157 p. | 1957 | 2016/03/25 | |||||||
魚類 | Cyprinus carpio (Carp) | Physiology | 12 | days | 100 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Taysse,L., D. Troutaud, N.A. Khan, and P. Deschaux | Structure-Activity Relationship of Phenolic Compounds (Phenol, Pyrocatechol and Hydroquinone) on Natural Lymphocytotoxicity of Carp (Cyprinus carpio) | Toxicology98(1-3): 207-214 | 1995 | 2016/03/25 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | No Group Code | 4 | hours | 5000 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Applegate,V.C., J.H. Howell, A.E.,Jr. Hall, and M.A. Smith | Toxicity of 4,346 Chemicals to Larval Lampreys and Fishes | Spec.Sci.Rep.Fish.No.207, Fish Wildl.Serv., U.S.D.I., Washington, DC:157 p. | 1957 | 2016/03/25 | |||||||
魚類 | Leuciscus idus (Orfe) | Mortality | LC0 | 2 | days | 100 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Juhnke,I., and D. Luedemann | Results of the Investigation of 200 Chemical Compounds for Acute Fish Toxicity with the Golden Orfe Test (Ergebnisse der Untersuchung von 200 Chemischen Verbindungen auf Akute Fischtoxizitat mit dem Goldorfentest) | Z. Wasser-Abwasser-Forsch.11(5): 161-164 | 1978 | 2018/03/15 | |||||
魚類 | Leuciscus idus (Orfe) | Mortality | LC100 | 2 | days | 200 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Juhnke,I., and D. Luedemann | Results of the Investigation of 200 Chemical Compounds for Acute Fish Toxicity with the Golden Orfe Test (Ergebnisse der Untersuchung von 200 Chemischen Verbindungen auf Akute Fischtoxizitat mit dem Goldorfentest) | Z. Wasser-Abwasser-Forsch.11(5): 161-164 | 1978 | 2018/03/15 | |||||
魚類 | Leuciscus idus (Orfe) | Mortality | LC50 | 2 | days | 150 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Juhnke,I., and D. Luedemann | Results of the Investigation of 200 Chemical Compounds for Acute Fish Toxicity with the Golden Orfe Test (Ergebnisse der Untersuchung von 200 Chemischen Verbindungen auf Akute Fischtoxizitat mit dem Goldorfentest) | Z. Wasser-Abwasser-Forsch.11(5): 161-164 | 1978 | 2018/03/15 | |||||
魚類 | Leuciscus idus (Orfe) | Mortality | LC50 | 2 | days | 160 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Juhnke,I., and D. Luedemann | Results of the Investigation of 200 Chemical Compounds for Acute Fish Toxicity with the Golden Orfe Test (Ergebnisse der Untersuchung von 200 Chemischen Verbindungen auf Akute Fischtoxizitat mit dem Goldorfentest) | Z. Wasser-Abwasser-Forsch.11(5): 161-164 | 1978 | 2018/03/15 | |||||
魚類 | Leuciscus idus (Orfe) | Mortality | LC100 | 2 | days | 250 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Juhnke,I., and D. Luedemann | Results of the Investigation of 200 Chemical Compounds for Acute Fish Toxicity with the Golden Orfe Test (Ergebnisse der Untersuchung von 200 Chemischen Verbindungen auf Akute Fischtoxizitat mit dem Goldorfentest) | Z. Wasser-Abwasser-Forsch.11(5): 161-164 | 1978 | 2018/03/15 | |||||
魚類 | Leuciscus idus (Orfe) | Mortality | LC0 | 2 | days | 100 | μg/L | FORMULATION | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Juhnke,I., and D. Luedemann | Results of the Investigation of 200 Chemical Compounds for Acute Fish Toxicity with the Golden Orfe Test (Ergebnisse der Untersuchung von 200 Chemischen Verbindungen auf Akute Fischtoxizitat mit dem Goldorfentest) | Z. Wasser-Abwasser-Forsch.11(5): 161-164 | 1978 | 2018/03/15 | |||||
魚類 | Danio rerio (Zebrafish) | Mortality | EC0 | 2 | days | 250 | μg/L | ACTIVE INGREDIENT | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lahnsteiner,F. | The Sensitivity and Reproducibility of the Zebrafish (Danio rerio) Embryo Test for the Screening of Waste Water Quality and for Testing the Toxicity of Chemicals | Alt. Lab. Anim. (ATLA)36(3): 299-311 | 2008 | 2018/03/09 | |||||
魚類 | Pimephales promelas (Fathead minnow) | mortality | LC50 | 96 | hours | 0.044 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | DeGraeve GM, Geiger DL, Meyer JS, Bergman HL | Acute and embryolarval toxicity of phenolic compounds to aquatic biota. | Arch Environm Contam Toxcol | 1980 | 2016/02/17 | ||||
魚類 | Pimephales promelas (Fathead minnow) | 死亡 | LC50 | 96 | hours | >0.4 | mg/L | × | 11 Japan チャレンジプログラム | Terhaar, C.J., Ewell, W.S., Dziuba, S.P., and Fassett, D.W. | Toxicity of Photographic Processing Chemicals to Fish | Phot. Sci. Eng. 16 | 1972 | 2016/03/09 | |||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 0.097 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | DeGraeve GM, Geiger DL, Meyer JS, Bergman HL | Acute and embryolarval toxicity of phenolic compounds to aquatic biota. | Arch Environm Contam Toxicol | 1980 | 2016/02/17 | ||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 97 | 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 | DeGraeve, G.M., D.L. Geiger, J.S. Meyer, and H.L. Bergman | Acute and Embryo-Larval Toxicity of Phenolic Compounds to Aquatic Biota. | Arch. Environ. Contam. Toxicol. (U.S.EPA「AQUIRE」) | 1980 | 2018/03/17 | |||||
魚類 | Brachydanio rerio (Zebrafish) | LC50 | 96 | hours | 0.17 | mg/L | 10 EHC (Environmental Health Criteria) | Wellens H | Comparison of the sensitivity of Brachydanio rerio and Leuciscus idus by testing the fish toxicity of chemicals and wastewaters. | Z Wasser Abwasser Forsch | 1982 | 2016/03/04 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.044 | mg/L | 18 既存化学物質安全性(ハザード)評価シート | US EPA | AQUIRE(ECOTOX Database System) | 2016/02/23 | |||||||||
魚類 | Leuciscus idus (Orfe) | LC100 | 48 | hours | 0.25 | mg/L | 10 EHC (Environmental Health Criteria) | Juhnke I & Lüdemann D | Results of the testing of 200 chemical compounds for acute toxicity for fish by means of the golden orfe test. | Z Wasser Abwasser Forsch | 1978 | 2016/03/04 | |||||||
魚類 | Leuciscus idus (Orfe) | LC50 | 48 | hours | 0.15 | mg/L | 10 EHC (Environmental Health Criteria) | Juhnke I & Lüdemann D | Results of the testing of 200 chemical compounds for acute toxicity for fish by means of the golden orfe test. | Z Wasser Abwasser Forsch | 1978 | 2016/03/04 | |||||||
魚類 | Lepomis macrochirus (Bluegill) | 100% mortality | LC100 | 22 | hours | 5 | mg/L | 10 EHC (Environmental Health Criteria) | US EPA | Part 1: The toxicity of 3400 chemicals to fish. Part 2: The toxicity of 1085 chemicals to fish. | Washington, DC, US Environmental Protection Agency, Office of Toxic Substances (EPA 560/6-87-002. | 1987 | 2016/03/04 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | 100% mortality | LC100 | 2 | hours | 7.69 | mg/L | 10 EHC (Environmental Health Criteria) | Devillers J, Boule P, Vasseur P, Prevot P, Steiman R, Seigle-Murandi F, Benoit-Guyod JL, Nendza M, Grioni C, Dive D, & Chambon P | Environmental and health risks of hydroquinone. | Ecotoxicol Environ Saf | 1990 | 2016/03/04 | ||||||
魚類 | Brachydanio rerio (Zebrafish) | LC0 | 96 | hours | 0.12 | mg/L | 10 EHC (Environmental Health Criteria) | Wellens H | Comparison of the sensitivity of Brachydanio rerio and Leuciscus idus by testing the fish toxicity of chemicals and wastewaters. | Z Wasser Abwasser Forsch | 1982 | 2016/03/04 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 0.044 | mg/L | 18 既存化学物質安全性(ハザード)評価シート | EU | IUCLID(International Uniform Chemical Information Data Base) Data Sheet | 1995 | 2016/02/23 | ||||||||
魚類 | Brachydanio rerio (Zebrafish) | LC50 | 24 | hours | 0.265 | mg/L | 10 EHC (Environmental Health Criteria) | Devillers J, Zakarya D, & Chastrette M | Structure-activity relationships for the toxicity of organic pollutants to Brachydanio rerio. | Turner JE, England MW, Schultz TW, & Kwaak NJ ed. Proceedings of the Third International Workshop on Quantitative Structure-Activity Relationships in Environmental Toxicology. | 1988 | 2018/03/14 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | 100% mortality | LC100 | 4 | hours | 4.5 | mg/L | 10 EHC (Environmental Health Criteria) | Devillers J, Boule P, Vasseur P, Prevot P, Steiman R, Seigle-Murandi F, Benoit-Guyod JL, Nendza M, Grioni C, Dive D, & Chambon P | Environmental and health risks of hydroquinone. | Ecotoxicol Environ Saf | 1990 | 2016/03/04 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 0.044 | mg/L | 10 EHC (Environmental Health Criteria) | DeGraeve GM, Geiger DL, Meyer JS, Bergman HL | Acute and embryo-larval toxicity of phenolic compounds to aquatic biota. | Arch Environ Contam Toxicol | 1980 | 2016/03/04 | |||||||
魚類 | Brachydanio rerio (Zebrafish) | LC100 | 96 | hours | 0.25 | mg/L | 10 EHC (Environmental Health Criteria) | Wellens H | Comparison of the sensitivity of Brachydanio rerio and Leuciscus idus by testing the fish toxicity of chemicals and wastewaters. | Z Wasser Abwasser Forsch | 1982 | 2016/03/04 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.639 | mg/L | 10 EHC (Environmental Health Criteria) | Hodson PV, Dixon DG, & Kaiser KLE | Measurement of median lethal dose as a rapid indication of contaminant toxicity to fish. | Environ Toxicol Chem | 1984 | 2016/03/04 | |||||||
魚類 | Carassius auratus (Goldfish) | LC100 | 48 | hours | 0.287 | mg/L | 10 EHC (Environmental Health Criteria) | Sollmann T | Correlation of the aquarium goldfish toxicities of some phenols, quinones and other benzene derivatives with their inhibition of autooxidative reactions. | J Gen Physiol | 1949 | 2016/03/04 | |||||||
魚類 | Leuciscus idus (Orfe) | LC0 | 48 | hours | 0.1 | mg/L | 10 EHC (Environmental Health Criteria) | Juhnke I & Lüdemann D | Results of the testing of 200 chemical compounds for acute toxicity for fish by means of the golden orfe test. | Z Wasser Abwasser Forsch | 1978 | 2016/03/04 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | LT50 | 11 | hours | 0.2 | mg/L | 10 EHC (Environmental Health Criteria) | Terhaar CJ, Ewell WS, Dziuba SP, & Fassett DW | Toxicity of photographic processing chemicals to fish. | Photogr Sci Eng | 1972 | 2018/03/13 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LD50 | 96 | hours | 24.2 | mg/kg | 10 EHC (Environmental Health Criteria) | Hodson PV, Dixon DG, & Kaiser KLE | Measurement of median lethal dose as a rapid indication of contaminant toxicity to fish. | Environ Toxicol Chem | 1984 | 2016/03/04 | |||||||
魚類 | Leuciscus idus (Orfe) | LC50 | 48 | hours | 0.16 | mg/L | 10 EHC (Environmental Health Criteria) | Juhnke I & Lüdemann D | Results of the testing of 200 chemical compounds for acute toxicity for fish by means of the golden orfe test. | Z Wasser Abwasser Forsch | 1978 | 2016/03/04 | |||||||
魚類 | Leuciscus idus (Orfe) | LC0 | 48 | hours | 0.1 | mg/L | 10 EHC (Environmental Health Criteria) | Juhnke I & Lüdemann D | Results of the testing of 200 chemical compounds for acute toxicity for fish by means of the golden orfe test. | Z Wasser Abwasser Forsch | 1978 | 2016/03/04 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.097 | mg/L | 10 EHC (Environmental Health Criteria) | DeGraeve GM, Geiger DL, Meyer JS, Bergman HL | Acute and embryo-larval toxicity of phenolic compounds to aquatic biota. | Arch Environ Contam Toxicol | 1980 | 2016/03/04 | |||||||
魚類 | Carassius auratus (Goldfish) | 100% mortality | LC100 | 22 | hours | 5 | mg/L | 10 EHC (Environmental Health Criteria) | US EPA | Part 1: The toxicity of 3400 chemicals to fish. Part 2: The toxicity of 1085 chemicals to fish. | Washington, DC, US Environmental Protection Agency, Office of Toxic Substances (EPA 560/6-87-002. | 1987 | 2016/03/04 | ||||||
魚類 | Leuciscus idus (Orfe) | LC100 | 48 | hours | 0.2 | mg/L | 10 EHC (Environmental Health Criteria) | Juhnke I & Lüdemann D | Results of the testing of 200 chemical compounds for acute toxicity for fish by means of the golden orfe test. | Z Wasser Abwasser Forsch | 1978 | 2016/03/04 | |||||||
魚類 | Danio rerio (Zebrafish) | LC50 | 24 | hours | 0.47 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Rhone poulenc | (EU, 2000から引用) | 1978 | 2018/03/22 | ||||||||
魚類 | Pimephales promelas (Fathead minnow) | Mortality | LC50 | 4 | days | 44 | 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 | DeGraeve, G.M., D.L. Geiger, J.S. Meyer, and H.L. Bergman | Acute and Embryo-Larval Toxicity of Phenolic Compounds to Aquatic Biota. | Arch. Environ. Contam. Toxicol. (U.S.EPA「AQUIRE」) | 1980 | 2018/03/17 | |||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 0.044 | mg/L | 8 NITE 化学物質の初期リスク評価書 | DeGraeve, G, M., Geiger, D.L., Meyer, J.S. and Bergman, H.L. | Acute and embryo-larval toxicity of phenolic compounds to aquatic viota. | Arch.Environ.Contam. Toxicol. | 1980 | 2018/03/18 | |||||||
魚類 | Danio rerio (Zebrafish) | LC50 | 96 | hours | 0.17 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Wellens, H. | Comparison of the sensitivity of Brachydanio rerio and Leuciscus idus by testing the fish toxicity of chemicals and wastewaters. | Z.wasser-Forsch. | 1982 | 2018/03/18 | |||||||
魚類 | Carassius auratus (Goldfish) | 致死 | LC100 | 48 | hours | >0.287 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Sollmann, T. | Correlation of the aquarium goldfish toxicities of some phenols, quinones, and other benzene derivatives with their inhibition of autooxidative reactions. | J.Gen.Physiol. | 1949 | 2018/03/18 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | >0.4 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Terhaar, C.J., Ewell, W.S., Dziuba, S.P. and Fassett, D.W. | Toxicity of photographic processing chemicals to fish. | Photogr.Sci.Eng. | 1972 | 2018/03/18 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC0 | 48 | hours | 0.1 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Lysak, A. and J. Marcinek. | Multiple toxic effect of simultaneous action of some chemical substances on fish. | Rocz.Nauk Roln.Ser.H Rybactwo | 1972 | 2018/03/18 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.097 | mg/L | 8 NITE 化学物質の初期リスク評価書 | DeGraeve, G, M., Geiger, D.L., Meyer, J.S. and Bergman, H.L. | Acute and embryo-larval toxicity of phenolic compounds to aquatic viota. | Arch.Environ.Contam. Toxicol. | 1980 | 2018/03/18 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.639 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Hodson, P.V., D.G. and Kaiser, K.L.E. | Measurement of median lethal dose as a rapid indication of contaminant toxicity to fish. | Environ. Toxicol. Chem. | 1984 | 2018/03/18 | |||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | LC100 | 48 | hours | >0.4 | mg/L | 8 NITE 化学物質の初期リスク評価書 | Lysak, A. and J. Marcinek. | Multiple toxic effect of simultaneous action of some chemical substances on fish. | Rocz.Nauk Roln.Ser.H Rybactwo | 1972 | 2018/03/18 | |||||||
魚類 | Leuciscus idus (Orfe) | Mortality | LC50 | 96 | hours | 0.149 | 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 | 0.0438 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Eldred, D.V., Weikel C.L., Jurs P.C., and Kaiser K.L.E. | Prediction of fathead minnow acute toxicity of organic compounds from molecular structure. | 1999 | 2016/02/08 | |||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 0.1~0.18 | × | 4 OECD SIDS (HPVC) | National Association of Photographic Manufacturers, Inc.,Environmental Effects of Photoprocessing Chemicals | National Association of Photographic Manufacturers, Inc., | 1974 | 2018/03/10 | ||||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | >0.4 | mg/L | × | 4 OECD SIDS (HPVC) | Terhaar, C.J., Ewell, W.S., Dziuba, S.P., and Fassett, D.W. | Toxicity of Photographic Processing Chemicals to Fish | Phot. Sci. Eng. | 1972 | 2018/03/10 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 96 | hours | 0.638 | mg/L | 12 ECHA Information on Registered Substances | 2 | Hodson PV, Dixon DG, Kaiser KLE | Measurement of median lethal dose as a rapid indication of contaminant toxicity to fish. | Environ Toxicol Chem | 1984 | 2018/02/24 | |||||
魚類 | Brachydanio rerio (Zebrafish) | LC50 | 96 | hours | 0.17 | mg/L | × | 4 OECD SIDS (HPVC) | Wellens, H. | Comparison of the Sensitivity of Brachydanio rerio and Leuciscus idus in the Study of the Toxicity to Fish of Chemical Compounds and Wastewaters | Z. Wasser Abwasser Forsch. | 1982 | 2018/03/10 | ||||||
魚類 | Oncorhynchus mykiss (Rainbow trout) | Lethal | EC50 | 96 | hours | 0.638 | mg/L | 9 ECETOC Aquatic Toxicity, EAT | Hodson ea 84 | 2018/03/22 | |||||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 0.044 | mg/L | 4 OECD SIDS (HPVC) | U.S. Environmental Protection Agency, | Pre-SIAR meeting comments. | 1995 | 2018/03/10 | ||||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | >0.4 | mg/L | × | 4 OECD SIDS (HPVC) | Terhaar, C.J., Ewell, W.S., Dziuba, S.P., and Fassett, D.W. | Toxicity of Photographic Processing Chemicals to Fish | Phot. Sci. Eng | 1972 | 2016/02/19 | ||||||
魚類 | Brachydanio rerio (Zebrafish) | LC50 | 96 | hours | 0.17 | mg/L | × | 4 OECD SIDS (HPVC) | Wellens, H | Comparison of the Sensitivity of Brachydanio rerio and Leuciscus idus in the Study of the Toxicity to Fish of Chemical Compounds and Wastewaters | Z. Wasser Abwasser Forsch | 1982 | 2016/02/19 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | 0.1~0.18 | × | 4 OECD SIDS (HPVC) | National Association of Photographic Manufacturers, Inc | Environmental Effects of Photoprocessing Chemicals | 1974 | 2016/02/19 | ||||||||
魚類 | Pimephales promelas (Fathead minnow) | reproduction | NOEC | 32 | days | >=66 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2016 | 2018/01/30 | ||||||
魚類 | Pimephales promelas (Fathead minnow) | reproduction | NOEC | 32 | days | >=100 | μg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2016 | 2018/01/30 |