【注意事項】
* 化学物質有害性情報データベース情報更新日が2019年9月以前はRead-acrossデータでも○としていないので、毒性値の取り扱いには注意が必要である。
| 生物種 | 学名 | 影響内容 | エンドポイント | 暴露期間(値) | 暴露期間(単位) | 毒性値 | 毒性値(単位) | Read-across * | QSAR | GLP | 設定濃度 | 実測濃度 | 情報源 | 情報源による信頼性評価 | 著者 | タイトル | 記載誌 | 発行年 | 情報更新日 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| subject type | scientific name | effect | endpoint | exposure duration value | exposure duration unit | toxicity value | toxicity unit | Read-across | QSAR | GLP | nominal concentration | measured concentration | original work type | original work reliability rank | author | title | referenced journal | publication year | Information update date |
| 藻類 | Chlorella vulgaris | Physiology | EC50 | 3 | hours | 107 | その他others [mmol/m3] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.C., J.A. Hellebust, D. Tam, D. Mackay, R.A. Mascarenhas, and W.Y. Shiu | The Correlation of the Toxicity to Algae of Hydrocarbons and Halogenated Hydrocarbons with Their Physical-Chemical Properties | Environ. Sci. Res.16:577-586 | 1980 | 2016/03/25 | ||||||
| 藻類 | Chlorella vulgaris | Physiology (Photosynthesis) | EC50 | 0.12 | days | 10.506137 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.C., J.A. Hellebust, D. Tam, D. Mackay, R.A. Mascarenhas, and W.Y. Shiu | The Correlation of the Toxicity to Algae of Hydrocarbons and Halogenated Hydrocarbons with Their Physical-Chemical Properties | Environ. Sci. Res.16:577-586 | 1980 | 2019/02/13 | ||||||
| 藻類 | others Chlamydomonas angulosa | Physiology (Photosynthesis) | EC50 | 0.12 | days | 10.506137 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.C., J.A. Hellebust, D. Tam, D. Mackay, R.A. Mascarenhas, and W.Y. Shiu | The Correlation of the Toxicity to Algae of Hydrocarbons and Halogenated Hydrocarbons with Their Physical-Chemical Properties | Environ. Sci. Res.16:577-586 | 1980 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | 生長速度 | ErC50 | 72 | hours | 0.336 | mg/L | ○ | 対照区, 助剤対照区, 0.32, 0.60, 1.2, 2.2, 4.2, 8.0mg/l | 0.0143, 0.0296, 0.0666, 0.128, 0.211, 0.351mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth rate | ErC50 | 72 | hours | 0.34 | mg/L | 4 OECD SIDS (HPVC) | 2020/01/17 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 0.34 | mg/L | 0.32, 0.60, 1.2, 2.2, 4.2, 8.0mg/l | 0.014, 0.030, 0.067, 0.13, 0.21, 0.35mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート（三監No.213） | 2020/01/08 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.134 | mg/L | ○ | control; solvent control; 0.32; 0.6; 1.2; 2.2; 4.2, 8.0 mg/L | control; solvent control; 0.0143; 0.0296; 0.0666; 0.128; 0.211, 0.351 mg/L (time-weighted average) | 12 ECHA Information on Registered Substances | 2 | study report | 2008 | |||||
| 藻類 | Chlorella vulgaris | PhysiologyPhotosynthesis | EC50 EC50/ | 3 | hours | 107 | mmol/m3 [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Hutchinson,T.C., J.A. Hellebust, D. Tam, D. Mackay, R.A. Mascarenhas, and W.Y. Shiu | The Correlation of the Toxicity to Algae of Hydrocarbons and Halogenated Hydrocarbons with Their Physical-Chemical Properties | Environ. Sci. Res.16 | 1980 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | 生長阻害 | EC50 | 72 | hours | 0.34 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | 生態影響試験（藻類、甲殻類、魚類）結果一覧(平成30年3月版） | 2018/12/19 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | 0.34 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | （Ⅱ-1）生態影響試験（藻類、甲殻類、魚類）結果一覧(平成27年3月版） | 2016/11/10 | |||||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | ErC50 | 72 | hours | 0.34 | mg/L | 4 OECD SIDS (HPVC) | CoCAM 6 | 2016/02/22 | |||||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | ErC50 | 72 | hours | 0.63 | mg/L | 4 OECD SIDS (HPVC) | CoCAM 6 | 2016/02/22 | |||||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | EC50 | 72 | hours | 0.134 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2008 | 2016/03/18 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth rate | NOErC | 72 | hours | 0.067 | mg/L | 4 OECD SIDS (HPVC) | 2020/01/17 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 0.067 | mg/L | 0.32, 0.60, 1.2, 2.2, 4.2, 8.0mg/l | 0.014, 0.030, 0.067, 0.13, 0.21, 0.35mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート（三監No.213） | 2020/01/08 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | 生長速度 | NOErC | 72 | hours | 0.0666 | mg/L | ○ | 対照区, 助剤対照区, 0.32, 0.60, 1.2, 2.2, 4.2, 8.0mg/l | 0.0143, 0.0296, 0.0666, 0.128, 0.211, 0.351mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/24 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 0.022 | mg/L | ○ | control; solvent control; 0.32; 0.6; 1.2; 2.2; 4.2, 8.0 mg/L | control; solvent control; 0.0143; 0.0296; 0.0666; 0.128; 0.211, 0.351 mg/L (time-weighted average) | 12 ECHA Information on Registered Substances | 2 | study report | 2008 | |||||
| 藻類 | Pseudokirchneriella subcapitata | 生長阻害 | NOEC | 72 | hours | 0.067 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | 生態影響試験（藻類、甲殻類、魚類）結果一覧(平成30年3月版） | 2018/12/19 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 0.067 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | （Ⅱ-1）生態影響試験（藻類、甲殻類、魚類）結果一覧(平成27年3月版） | 2016/11/10 | |||||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | NOErC | 72 | hours | 0.22 | mg/L | 4 OECD SIDS (HPVC) | CoCAM 6 | 2016/02/22 | |||||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | NOErC | 72 | hours | 0.067 | mg/L | 4 OECD SIDS (HPVC) | CoCAM 6 | 2016/02/22 | |||||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | 72 | hours | 0.0221 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | study report | 2008 | 2016/03/18 | |||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 1.486031 | その他others [mol/L] | 17 Aquatic OASIS (OECD QSAR Toolbox) | Abernethy, A.M., Bobra, W.Y., Shiu, P.G., Wells and Mackay. | Acute lethal toxicity of hydrocarbons and chlorinated hydrocarbons to two planktonic crustaceans: the key role of organism-partitioning. | Aquatic Toxicity, 8 | 1986 | 2019/02/22 | ||||||
| 甲殻類 | Daphnia magna | Intoxication | EC50 | 24 | hours | 1.520646 | その他others [mol/L] | 17 Aquatic OASIS (OECD QSAR Toolbox) | Urrestarazu Ramos, E. | Aquatic toxicity of polar narcotic pollutants/ Mechanism, modeling and environmental effect assessment (PhD Thesis) | ISBN 90-393-1638-4 | 1998 | 2019/02/22 | ||||||
| 甲殻類 | Daphnia magna | Physiology | EC50 | 2 | days | 15 | その他others [mmol/m3] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bobra,A.M., W.Y. Shiu, and D. Mackay | A Predictive Correlation for the Acute Toxicity of Hydrocarbons and Chlorinated Hydrocarbons to the Water Flea (Daphnia magna) | Chemosphere12(9-10): 1121-1129 | 1983 | 2016/03/25 | ||||||
| 甲殻類 | others Crangon franciscorum | Mortality | LC50 | 4 | days | 3.3 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Benville,P.E.,Jr., J.A. Whipple, and M.B. Eldridge | Acute Toxicity of Seven Alicyclic Hexanes to Striped Bass, Morone saxatilis, and Bay Shrimp, Crangon franciscorum, in Seawater | Calif. Fish Game71(3): 132-140 | 1985 | 2019/02/13 | ||||||
| 甲殻類 | others Crangon franciscorum | Mortality | LC50 | 1 | days | 3.5 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Benville,P.E.,Jr., J.A. Whipple, and M.B. Eldridge | Acute Toxicity of Seven Alicyclic Hexanes to Striped Bass, Morone saxatilis, and Bay Shrimp, Crangon franciscorum, in Seawater | Calif. Fish Game71(3): 132-140 | 1985 | 2019/02/13 | ||||||
| 甲殻類 | others Cyclops viridis | Mortality | LC50 | 4 | days | 865 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Panigrahi,A.K., and S.K. Konar | Acute Toxicity of Some Petroleum Pollutants to Plankton, Fish and Benthic Organism | Environ. Ecol.7(1): 44-49 | 1989 | 2019/02/13 | ||||||
| 甲殻類 | others Artemia salina | Mortality | LC50 | 1 | days | 3.682057 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Abernethy,S., A.M. Bobra, W.Y. Shiu, P.G. Wells, and D. Mackay | Acute Lethal Toxicity of Hydrocarbons and Chlorinated Hydrocarbons to Two Planktonic Crustaceans: The Key Role of Organism-Water Partitioning | Aquat. Toxicol.8(3): 163-174 | 1986 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | EC50 | 2 | days | 1.472823 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bobra,A.M., W.Y. Shiu, and D. Mackay | A Predictive Correlation for the Acute Toxicity of Hydrocarbons and Chlorinated Hydrocarbons to the Water Flea (Daphnia magna) | Chemosphere12(9-10): 1121-1129 | 1983 | 2019/02/13 | ||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 0.33 | mg/L | 4 OECD SIDS (HPVC) | 2020/01/17 | |||||||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 0.33 | mg/L | 0.050, 0.10, 0.20, 0.40, 0.80mg/l | 0.037, 0.080, 0.15, 0.30, 0.60mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート（三監No.213） | 2020/01/08 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.326 | mg/L | ○ | control; solvent control; 0.05; 0.1; 0.2; 0.4, 0.8 mg/L | control; solvent control; 0.037; 0.08; 0.153; 0.298, 0.603 mg/L (time weighted average concentrations) | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Mortality | LC50 | 48 | hours | 0.0151 | mmol/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Abernethy, A.M., Bobra, W.Y., Shiu, P.G., Wells and Mackay. | Acute lethal toxicity of hydrocarbons and chlorinated hydrocarbons to two planktonic crustaceans: the key role of organism-partitioning. | Aquatic Toxicity, 8 | 1986 | ||||||||
| 甲殻類 | Daphnia magna | Immobilization | EC100 | 48 | hours | 0.603 | mg/L | ○ | 対照区, 助剤対照区, 0.050, 0.10, 0.20, 0.40, 0.80mg/l | 0.037, 0.080, 0.153, 0.298, 0.603mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | |||||||
| 甲殻類 | Daphnia magna | Immobilization | EC0 | 48 | hours | 0.037 | mg/L | ○ | 対照区, 助剤対照区, 0.050, 0.10, 0.20, 0.40, 0.80mg/l | 0.037, 0.080, 0.153, 0.298, 0.603mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | |||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 24 | hours | >0.603 | mg/L | ○ | 対照区, 助剤対照区, 0.050, 0.10, 0.20, 0.40, 0.80mg/l | 0.037, 0.080, 0.153, 0.298, 0.603mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | |||||||
| 甲殻類 | Daphnia magna | EC50 | 24 | hours | >0.603 | mg/L | ○ | control; solvent control; 0.05; 0.1; 0.2; 0.4, 0.8 mg/L | control; solvent control; 0.037; 0.08; 0.153; 0.298, 0.603 mg/L (time weighted average concentrations) | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC0 | 48 | hours | 0.037 | mg/L | ○ | control; solvent control; 0.05; 0.1; 0.2; 0.4, 0.8 mg/L | control; solvent control; 0.037; 0.08; 0.153; 0.298, 0.603 mg/L (time weighted average concentrations) | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Daphnia magna | mobility | EC100 | 48 | hours | 0.603 | mg/L | ○ | control; solvent control; 0.05; 0.1; 0.2; 0.4, 0.8 mg/L | control; solvent control; 0.037; 0.08; 0.153; 0.298, 0.603 mg/L (time weighted average concentrations) | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 甲殻類 | Intoxication | EC50 | 24 | hours | 0.0155 | mmol/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Urrestarazu Ramos, E. | Aquatic toxicity of polar narcotic pollutants/ Mechanism, modeling and environmental effect assessment (PhD Thesis) | ISBN 90-393-1638-4 | 1998 | ||||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 48 | hours | 0.326 | mg/L | ○ | 対照区, 助剤対照区, 0.050, 0.10, 0.20, 0.40, 0.80mg/l | 0.037, 0.080, 0.153, 0.298, 0.603mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | |||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 48 | hours | 15 | mmol/m3 [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Bobra,A.M., W.Y. Shiu, and D. Mackay | A Predictive Correlation for the Acute Toxicity of Hydrocarbons and Chlorinated Hydrocarbons to the Water Flea (Daphnia magna) | Chemosphere12(9-10) | 1983 | |||||||
| 甲殻類 | Daphnia magna | 遊泳阻害 | EC50 | 48 | hours | 0.33 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | 生態影響試験（藻類、甲殻類、魚類）結果一覧(平成30年3月版） | 2018/12/19 | ||||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 0.33 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | （Ⅱ-1）生態影響試験（藻類、甲殻類、魚類）結果一覧(平成27年3月版） | 2016/11/10 | |||||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 0.67 | mg/L | 4 OECD SIDS (HPVC) | CoCAM 6 | 2016/02/22 | ||||||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 0.33 | mg/L | 4 OECD SIDS (HPVC) | CoCAM 6 | 2016/02/22 | ||||||||||
| 甲殻類 | Daphnia magna | EC50 | 24 | hours | >0.603 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2008 | 2019/02/20 | ||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 48 | hours | 1.49 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Abernethy, A.M., Bobra, W.Y., Shiu, P.G., Wells and Mackay. | Acute lethal toxicity of hydrocarbons and chlorinated hydrocarbons to two planktonic crustaceans: the key role of organism-partitioning. | 1986 | 2016/02/08 | |||||||
| 甲殻類 | Daphnia magna | Intoxication | ET50 | 24 | hours | 1.52 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Urrestarazu Ramos, E. | Aquatic toxicity of polar narcotic pollutants/ Mechanism, modeling and environmental effect assessment (PhD Thesis) | 1998 | 2016/02/08 | |||||||
| 甲殻類 | Daphnia magna | EC50 | 24 | hours | >0.603 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.326 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC100 | 48 | hours | 0.603 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC0 | 48 | hours | 0.037 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | ||||||
| 魚類 | number hatched | NOEC | 7 | days | >=0.83 | mg/L | × | flagfish: control, 0.34 (± 0.38), 0.67 (± 0.65), 0.83 (± 0.73) mg/L as dissolved test substance rainbow trout: control, 0.31, 0.80, 0.84, 1.19 mg/L | 12 ECHA Information on Registered Substances | 3 | study report | 1976 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 23 | days | 1.3 | mg/L [meas.(arithm.mean) Test substance] | × | 0.31, 0.80, 0.84 and 1.19 mg/L as dissolved test substance | 12 ECHA Information on Registered Substances | 3 | study report | 1976 | 2020/03/18 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 23 | days | 1300 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In | 1975 | |||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 48 | hours | 5.035332 | その他others [mol/L] | 17 Aquatic OASIS (OECD QSAR Toolbox) | Unnamed | Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan | Chemicals Investigation and Testing Institute. 1992. Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan, ISBN 4-98074-101-1. Japan Chemical Industry Ecology-Toxicology&Information Center | 1992 | 2019/02/22 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | No Group Code | 13 | 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 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 23 | days | 1300 | μg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2016/03/25 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 4 | days | 180 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 3 | days | 41 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 4 | days | 235000 | その他others [L, Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 2 | days | 41 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 23 | days | 1.3 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Chironomidae | Mortality | LC50 | 4 | days | 1000 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Panigrahi,A.K., and S.K. Konar | Acute Toxicity of Some Petroleum Pollutants to Plankton, Fish and Benthic Organism | Environ. Ecol.7(1): 44-49 | 1989 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 4 | days | 62 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 2 | days | 62 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 4 | days | 41 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 2 | days | 97 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Melanoides tuberculata | Mortality | LC50 | 4 | days | 1160 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Panigrahi,A.K., and S.K. Konar | Acute Toxicity of Some Petroleum Pollutants to Plankton, Fish and Benthic Organism | Environ. Ecol.7(1): 44-49 | 1989 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 3 | days | 180 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 3 | days | 69 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Morone saxatilis | Mortality | LC50 | 4 | days | 5.8 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Benville,P.E.,Jr., J.A. Whipple, and M.B. Eldridge | Acute Toxicity of Seven Alicyclic Hexanes to Striped Bass, Morone saxatilis, and Bay Shrimp, Crangon franciscorum, in Seawater | Calif. Fish Game71(3): 132-140 | 1985 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 1 | days | 41 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Morone saxatilis | Mortality | LC50 | 1 | days | 7 | mg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Benville,P.E.,Jr., J.A. Whipple, and M.B. Eldridge | Acute Toxicity of Seven Alicyclic Hexanes to Striped Bass, Morone saxatilis, and Bay Shrimp, Crangon franciscorum, in Seawater | Calif. Fish Game71(3): 132-140 | 1985 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 3 | days | 184000 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 2 | days | 187000 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 3 | days | 62 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 2 | days | 180 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 1 | days | 62 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 1 | days | 238000 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 4 | days | 55 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | others Notemigonus crysoleucas | Mortality | LC50 | 1 | days | 180 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Klein,S.A., D. Jenkins, and R.C. Cooper | The Toxicity to Fish of the Jet Fuel JP-9, its Components RJ-4, RJ-5 and Methylcyclohexane (MCH) | In: Tech.Rep.AMRL-TR-75-125, Aerosp.Med.Res.Lab., Pap.No.24:429-455 | 1975 | 2019/02/13 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 2.1 | mg/L | 4 OECD SIDS (HPVC) | 2020/01/17 | |||||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 2.1 | mg/L | 2.0, 3.6, 6.3, 11, 20mg/l | 0.64, 1.2, 2.0, 3.3, 7.3mg/l | 18 既存化学物質安全性(ハザード)評価シート | 環境省 | 既存化学物質審査シート（三監No.213） | 2020/01/08 | |||||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | 2.07 | mg/L | ○ | control, vehicle control, 2.0, 3.6, 6.3, 11, 20 mg/L | control, vehicle control, 0.638, 1.18, 2.04, 3.26, 7.26 mg/L (time weighted mean) | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | |||||
| 魚類 | Mortality | LC50 | 48 | hours | 0.0513 | mmol/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan | Chemicals Investigation and Testing Institute. 1992. Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan, ISBN 4-98074-101-1. Japan Chemical Industry Ecology-Toxicology&Information Center; | 1992 | |||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 96 | hours | 2.07 | mg/L | ○ | 対照区, 助剤対照区, 2.0, 3.6, 6.3, 11, 20mg/l | 0.638, 1.18, 2.04, 3.26, 7.26mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | |||||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 48 | hours | 5.02 | mg/L | × | not available | 12 ECHA Information on Registered Substances | 2 | study report | 1986 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 72 | hours | 2.36 | mg/L | ○ | 対照区, 助剤対照区, 2.0, 3.6, 6.3, 11, 20mg/l | 0.638, 1.18, 2.04, 3.26, 7.26mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | ||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC100 | 96 | hours | 3.26 | mg/L | ○ | 対照区, 助剤対照区, 2.0, 3.6, 6.3, 11, 20mg/l | 0.638, 1.18, 2.04, 3.26, 7.26mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | |||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 48 | hours | 2.81 | mg/L | ○ | 対照区, 助剤対照区, 2.0, 3.6, 6.3, 11, 20mg/l | 0.638, 1.18, 2.04, 3.26, 7.26mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | ||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 24 | hours | 4.19 | mg/L | ○ | 対照区, 助剤対照区, 2.0, 3.6, 6.3, 11, 20mg/l | 0.638, 1.18, 2.04, 3.26, 7.26mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | ||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC0 | 96 | hours | 0.638 | mg/L | ○ | 対照区, 助剤対照区, 2.0, 3.6, 6.3, 11, 20mg/l | 0.638, 1.18, 2.04, 3.26, 7.26mg/l | 1 日本環境省 生態リスク初期評価 | 2020/01/22 | |||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 2.1 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | 生態影響試験（藻類、甲殻類、魚類）結果一覧(平成30年3月版） | 2018/12/19 | |||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 2.1 | mg/L | 1 日本環境省 生態リスク初期評価 | 環境省 | （Ⅱ-1）生態影響試験（藻類、甲殻類、魚類）結果一覧(平成27年3月版） | 2016/11/10 | |||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 2.1 | mg/L | 4 OECD SIDS (HPVC) | CoCAM 6 | 2016/02/22 | ||||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | LC50 | 96 | hours | 0.75 | mg/L | 4 OECD SIDS (HPVC) | CoCAM 6 | 2016/02/22 | ||||||||||
| 魚類 | Oryzias latipes (Japanese medaka) | Mortality | LC50 | 48 | hours | 5.04 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | - | Biodegradation and Bioaccumulation Data of Existing Chemicals Based on the CSCL Japan | 1992 | 2016/02/08 | |||||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 48 | hours | 5.02 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | study report | 1986 | 2016/03/18 | ||||||
| 魚類 | Oryzias latipes (Japanese medaka) | mortality | LC50 | 96 | hours | 2.07 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2008 | 2016/03/18 | ||||||
| 魚類 | Jordanella floridae | other: fry development | NOEC | 87 | days | >=0.83 | mg/L | × | flagfish: control, 0.34 (± 0.38), 0.67 (± 0.65), 0.83 (± 0.73) mg/L as dissolved test substance rainbow trout: control, 0.31, 0.80, 0.84, 1.19 mg/L | 12 ECHA Information on Registered Substances | 3 | study report | 1976 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 23 | days | 1.3 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | study report | Unnamed | 1976 | 2019/02/20 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | mortality | LC50 | 23 | days | 1.3 | mg/L | × | 12 ECHA Information on Registered Substances | 3 | study report | 1976 | 2016/03/18 |