【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 | Chlorella vulgaris | Basis for effect: growth rate | NOEC | 12 | weeks | 4000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1965 | 2022/07/19 | |||||
| 藻類 | Pseudokirchneriella subcapitata | Basis for effect: growth rate | NOEC | 72 | hours | >=30.1 | mgBa/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 藻類 | Pseudokirchneriella subcapitata | Basis for effect: growth rate | EC50 | 72 | hours | >85.3 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 藻類 | Pseudokirchneriella subcapitata | Basis for effect: growth rate | EC50 | 72 | hours | >1.15 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 藻類 | Chlorella vulgaris | Basis for effect: growth rate | LOEC | 12 | weeks | 8000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1965 | 2022/07/19 | |||||
| 藻類 | Pseudokirchneriella subcapitata | Basis for effect: growth rate | NOEC | 72 | hours | >=85.3 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 藻類 | Chlorella vulgaris | inhibitory effect on photo-autotrophic growth | LOEC | 15 | weeks | 8 | mg/L | 4 OECD SIDS (HPVC) | 3 | De Jong, L.E.D. | Tolerance of Chlorella vulgaris for Metallic and Non-Metallic Ions | Antonie Leeuwenhoek | 1965 | 2018/12/04 | |||||
| 藻類 | others Lemna minor | growth rate | EC50 | 96 | hours | 26～61 | 4 OECD SIDS (HPVC) | Wang W. | The Effect of River Water on Phytotoxicity of Ba, Cd and Cr, Environmental Pollution (Series B) 11 | 1986 | 2019/02/08 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | Basis for effect: growth rate | NOEC | 72 | hours | >=100 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 藻類 | Scenedesmus subspicatus | Population (Abundance) | NOEC | 8 | days | 5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Theegala,C.S., C. Robertson, P.E. Carriere, and A.A. Suleiman | Phytoremediation Potential and Toxicity of Barium to Three Freshwater Microalgae: Scenedesmus subspicatus, Selenastrum capricornutum, and Nannochloropsis sp. | Pract. Periodical Hazard. Toxic Radioact. Waste Manag.5(4): 194-202 | 2001 | 2019/02/13 | |||||
| 藻類 | Pseudokirchneriella subcapitata | Population (Abundance) | NOEC | 10 | days | 5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Theegala,C.S., C. Robertson, P.E. Carriere, and A.A. Suleiman | Phytoremediation Potential and Toxicity of Barium to Three Freshwater Microalgae: Scenedesmus subspicatus, Selenastrum capricornutum, and Nannochloropsis sp. | Pract. Periodical Hazard. Toxic Radioact. Waste Manag.5(4): 194-202 | 2001 | 2019/02/13 | |||||
| 藻類 | Pseudokirchneriella subcapitata | Basis for effect: growth rate | EC50 | 72 | hours | >30.1 | mgBa/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 藻類 | others Nannochloropsis sp. | Population (Abundance) | NOEC | 10 | days | 5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Theegala,C.S., C. Robertson, P.E. Carriere, and A.A. Suleiman | Phytoremediation Potential and Toxicity of Barium to Three Freshwater Microalgae: Scenedesmus subspicatus, Selenastrum capricornutum, and Nannochloropsis sp. | Pract. Periodical Hazard. Toxic Radioact. Waste Manag.5(4): 194-202 | 2001 | 2019/02/13 | |||||
| 藻類 | Chlorella vulgaris | inhibitory effect on photo-autotrophic growth | NOEC | 15 | weeks | 4 | mg/L | 4 OECD SIDS (HPVC) | 3 | De Jong, L.E.D. | Tolerance of Chlorella vulgaris for Metallic and Non-Metallic Ions | Antonie Leeuwenhoek | 1965 | 2018/12/04 | |||||
| 藻類 | Pseudokirchneriella subcapitata | Basis for effect: growth rate | EC50 | 72 | hours | >100 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 藻類 | Chlorella vulgaris | Population (Population changes, general) | LOEC | days | 8 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Jong,L.E.D. | Tolerance of Chlorella vulgaris for Metallic and Non-Metallic Ions | Antonie van Leeuwenhoek (Gedrukt)31:301-313 | 1965 | 2019/02/13 | ||||||
| 藻類 | Chlorella vulgaris | Population (Population changes, general) | NOEC | days | 4 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | De Jong,L.E.D. | Tolerance of Chlorella vulgaris for Metallic and Non-Metallic Ions | Antonie van Leeuwenhoek (Gedrukt)31:301-313 | 1965 | 2019/02/13 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Basis for effect: growth rate | NOEC | 72 | hours | >=1.15 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 藻類 | Chlorella vulgaris | inhibitory effect on photo-autotrophic growth | LOEC | 15 | weeks | 8 | mg/L | 4 OECD SIDS (HPVC) | 3 | De Jong, L.E.D. | Tolerance of Chlorella vulgaris for Metallic and Non-Metallic Ions | Antonie Leeuwenhoek | 1965 | 2018/12/04 | |||||
| 藻類 | Chlorella vulgaris | inhibitory effect on photo-autotrophic growth | NOEC | 15 | weeks | 4 | mg/L | 4 OECD SIDS (HPVC) | 3 | De Jong, L.E.D. | Tolerance of Chlorella vulgaris for Metallic and Non-Metallic Ions | Antonie Leeuwenhoek | 1965 | 2018/12/04 | |||||
| 藻類 | Raphidocelis subcapitata | growth rate | EC50 | 72 | hours | >30.1 | mg/L | meas. (geom. mean) element | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 藻類 | Raphidocelis subcapitata | growth rate | EC50 | 72 | hours | >1.15 | mg/L | meas. (geom. mean) dissolved | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 藻類 | Raphidocelis subcapitata | growth rate | EC50 | 72 | hours | >85.3 | mg/L | nominal barium dichloride | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 藻類 | Raphidocelis subcapitata | growth rate | EC50 | 72 | hours | >100 | mg/L | nominal test mat. | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 藻類 | Chlorella vulgaris | Population/Population changes, general | LOEC | 8000 | µg/L | Total | × | 16 ECOTOX | De Jong,L.E.D. | Tolerance of Chlorella vulgaris for Metallic and Non-Metallic Ions | Antonie van Leeuwenhoek (Gedrukt)31 | 2022/09/15 | |||||||
| 藻類 | Raphidocelis subcapitata | growth rate | NOEC | 72 | hours | >=85.3 | mg/L | nominal barium dichloride | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 藻類 | Scenedesmus quadricauda | turbidity | LOEC | 4 | days | 34000 | μg/L | nominal not specified | 12 ECHA Information on Registered Substances | 3 | Bringmann G and Kühn R | Vergleichende wasser-toxikologische Untersuchungen an Bakterien, Algen und Kleinkrebsen. | Gesundheits-Ingenieur heft 80, 1959 | 1959 | 2022/09/15 | ||||
| 藻類 | Chlorella vulgaris | growth rate | NOEC | 12 | weeks | 4000 | μg/L | nominal element | 12 ECHA Information on Registered Substances | 3 | publication | 1965 | 2022/09/15 | ||||||
| 藻類 | Desmodesmus subspicatus | Population/Abundance | NOEC | 8 | days | 5 | mg/L | Total | × | 16 ECOTOX | Theegala,C.S., C. Robertson, P.E. Carriere, and A.A. Suleiman | Phytoremediation Potential and Toxicity of Barium to Three Freshwater Microalgae: Scenedesmus subspicatus, Selenastrum capricornutum, and Nannochloropsis sp. | Pract. Period. Hazard. Toxic Radioact. Waste Manag.5(4) | 2022/09/15 | |||||
| 藻類 | Chlorella vulgaris | Population/Population changes, general | NOEC | 4000 | µg/L | Total | × | 16 ECOTOX | De Jong,L.E.D. | Tolerance of Chlorella vulgaris for Metallic and Non-Metallic Ions | Antonie van Leeuwenhoek (Gedrukt)31 | 2022/09/15 | |||||||
| 藻類 | Raphidocelis subcapitata | growth rate | NOEC | 72 | hours | >=30.1 | mg/L | meas. (geom. mean) element | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 藻類 | Raphidocelis subcapitata | growth rate | NOEC | 72 | hours | >=100 | mg/L | nominal test mat. | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 藻類 | Chlorella vulgaris | NOEC | 4 | mg/L | Ba | ○ | 10 EHC (Environmental Health Criteria) | Den Dooren de Jong, L.E. | Tolerance of Chlorella vulgaris for metallic and non-metallic ions | Antonie van Leeuwenhoek, 31 | 1965 | 2023/02/21 | |||||||
| 藻類 | Chlorella vulgaris | growth rate | LOEC | 12 | weeks | 8000 | μg/L | nominal element | 12 ECHA Information on Registered Substances | 3 | publication | 1965 | 2022/09/15 | ||||||
| 藻類 | Chlorella vulgaris | LOEC | 8 | mg/L | Ba | ○ | 10 EHC (Environmental Health Criteria) | Den Dooren de Jong, L.E. | Tolerance of Chlorella vulgaris for metallic and non-metallic ions | Antonie van Leeuwenhoek, 31 | 1965 | 2023/02/21 | |||||||
| 藻類 | Raphidocelis subcapitata | growth rate | NOEC | 72 | hours | >=1.15 | mg/L | meas. (geom. mean) dissolved | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 藻類 | Selenastrum capricornutum | Population/Abundance | NOEC | 10 | days | 5 | mg/L | Total | × | 16 ECOTOX | Theegala,C.S., C. Robertson, P.E. Carriere, and A.A. Suleiman | Phytoremediation Potential and Toxicity of Barium to Three Freshwater Microalgae: Scenedesmus subspicatus, Selenastrum capricornutum, and Nannochloropsis sp. | Pract. Period. Hazard. Toxic Radioact. Waste Manag.5(4) | 2022/09/15 | |||||
| 甲殻類 | others Scenedesmus quadricauda | Basis for effect: other: turbidity | LOEC | 4 | days | 34000 | μg/L | × | 12 ECHA Information on Registered Substances | 3 | Bringmann G and Kühn R | Vergleichende wasser-toxikologische Untersuchungen an Bakterien, Algen und Kleinkrebsen. | Gesundheits-Ingenieur heft 80 | 1959 | 2019/01/16 | ||||
| 甲殻類 | others green alga Gloeotaenium | Basis for effect: other: effect on calcification | LOEC | 96 | hours | 1000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1984 | 2019/01/16 | |||||
| 甲殻類 | Daphnia magna | 64 | hours | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1948 | 2019/01/16 | |||||||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | NOEC | 0.66 | days | 83 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,B.G. | The Toxicity Thresholds of Various Substances Found in Industrial Wastes as Determined by the Use of Daphnia magna | Sewage Works J.16(6): 1156-1165 | 1944 | 2019/02/13 | |||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | EC50 | 21 | days | 13.5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2019/02/13 | |||||
| 甲殻類 | others Austropotamobius pallipes ssp. pallipes | Mortality | LC50 | 4 | days | 46 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Boutet,C., and C. Chaisemartin | Specific Toxic Properties of Metallic Salts in Austro-potamobius pallipes pallipes and Orconectes limosus (Proprietes Toxiques Specifiques des sels Metalliques chez Austropotamobius pallipes pallipes et Orconectes limos | Comptes Rendus Seances Soc. Biol. Fil.167(12): 1933-1938 | 1973 | 2019/02/13 | |||||
| 甲殻類 | others Orconectes limosus | Mortality | LC50 | 30 | days | 61 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Boutet,C., and C. Chaisemartin | Specific Toxic Properties of Metallic Salts in Austro-potamobius pallipes pallipes and Orconectes limosus (Proprietes Toxiques Specifiques des sels Metalliques chez Austropotamobius pallipes pallipes et Orconectes limos | Comptes Rendus Seances Soc. Biol. Fil.167(12): 1933-1938 | 1973 | 2019/02/13 | |||||
| 甲殻類 | others Echinogammarus berilloni | Mortality | LC50 | 4 | days | 122 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vincent,M., B. Penicaut, and J. Debord | Comparative Studies on the Toxicity of Metal Chlorides and of a Synthetic Organic Molluscicide, N-Trityl-Morpholine, upon Two Aquatic Amphipod Crustaceans, Gammarus pulex and Echinogammarus berilloni | Ann. Rech. Vet.17(4): 441-446 | 1986 | 2019/02/13 | |||||
| 甲殻類 | others Echinogammarus berilloni | Mortality | LC50 | 2 | days | 258 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vincent,M., B. Penicaut, and J. Debord | Comparative Studies on the Toxicity of Metal Chlorides and of a Synthetic Organic Molluscicide, N-Trityl-Morpholine, upon Two Aquatic Amphipod Crustaceans, Gammarus pulex and Echinogammarus berilloni | Ann. Rech. Vet.17(4): 441-446 | 1986 | 2019/02/13 | |||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 1 | days | 3980 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vincent,M., B. Penicaut, and J. Debord | Comparative Studies on the Toxicity of Metal Chlorides and of a Synthetic Organic Molluscicide, N-Trityl-Morpholine, upon Two Aquatic Amphipod Crustaceans, Gammarus pulex and Echinogammarus berilloni | Ann. Rech. Vet.17(4): 441-446 | 1986 | 2019/02/13 | |||||
| 甲殻類 | others Orconectes limosus | Mortality | LC50 | 30 | days | 59 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Boutet,C., and C. Chaisemartin | Specific Toxic Properties of Metallic Salts in Austro-potamobius pallipes pallipes and Orconectes limosus (Proprietes Toxiques Specifiques des sels Metalliques chez Austropotamobius pallipes pallipes et Orconectes limos | Comptes Rendus Seances Soc. Biol. Fil.167(12): 1933-1938 | 1973 | 2019/02/13 | |||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | 4 | days | 29 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,B.G., T.F. Andrews, D.C. Chandler, and W.J. Jahoda | The Evaluation of Aquatic Invertebrates as Assay Organisms for the Determination of the Toxicity of Industrial Wastes | Final Report 51, American Petroleum Institute Project, Ohio State University, Columbus, OH: | 1948 | 2019/02/13 | ||||||
| 甲殻類 | others Cyclops vernalis | Intoxication (Immobile) | 4 | days | 123 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,B.G., T.F. Andrews, D.C. Chandler, and W.J. Jahoda | The Evaluation of Aquatic Invertebrates as Assay Organisms for the Determination of the Toxicity of Industrial Wastes | Final Report 51, American Petroleum Institute Project, Ohio State University, Columbus, OH: | 1948 | 2019/02/13 | ||||||
| 甲殻類 | others Leptodora kindtii | Intoxication (Immobile) | 4 | days | 12 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,B.G., T.F. Andrews, D.C. Chandler, and W.J. Jahoda | The Evaluation of Aquatic Invertebrates as Assay Organisms for the Determination of the Toxicity of Industrial Wastes | Final Report 51, American Petroleum Institute Project, Ohio State University, Columbus, OH: | 1948 | 2019/02/13 | ||||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 2 | days | 395 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vincent,M., B. Penicaut, and J. Debord | Comparative Studies on the Toxicity of Metal Chlorides and of a Synthetic Organic Molluscicide, N-Trityl-Morpholine, upon Two Aquatic Amphipod Crustaceans, Gammarus pulex and Echinogammarus berilloni | Ann. Rech. Vet.17(4): 441-446 | 1986 | 2019/02/13 | |||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 4 | days | 238 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vincent,M., B. Penicaut, and J. Debord | Comparative Studies on the Toxicity of Metal Chlorides and of a Synthetic Organic Molluscicide, N-Trityl-Morpholine, upon Two Aquatic Amphipod Crustaceans, Gammarus pulex and Echinogammarus berilloni | Ann. Rech. Vet.17(4): 441-446 | 1986 | 2019/02/13 | |||||
| 甲殻類 | others Gammarus pulex | Mortality | LC50 | 3 | days | 255 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vincent,M., B. Penicaut, and J. Debord | Comparative Studies on the Toxicity of Metal Chlorides and of a Synthetic Organic Molluscicide, N-Trityl-Morpholine, upon Two Aquatic Amphipod Crustaceans, Gammarus pulex and Echinogammarus berilloni | Ann. Rech. Vet.17(4): 441-446 | 1986 | 2019/02/13 | |||||
| 甲殻類 | others Echinogammarus berilloni | Mortality | LC50 | 1 | days | 336 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vincent,M., B. Penicaut, and J. Debord | Comparative Studies on the Toxicity of Metal Chlorides and of a Synthetic Organic Molluscicide, N-Trityl-Morpholine, upon Two Aquatic Amphipod Crustaceans, Gammarus pulex and Echinogammarus berilloni | Ann. Rech. Vet.17(4): 441-446 | 1986 | 2019/02/13 | |||||
| 甲殻類 | others Echinogammarus berilloni | Mortality | LC50 | 3 | days | 162 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Vincent,M., B. Penicaut, and J. Debord | Comparative Studies on the Toxicity of Metal Chlorides and of a Synthetic Organic Molluscicide, N-Trityl-Morpholine, upon Two Aquatic Amphipod Crustaceans, Gammarus pulex and Echinogammarus berilloni | Ann. Rech. Vet.17(4): 441-446 | 1986 | 2019/02/13 | |||||
| 甲殻類 | others Austropotamobius pallipes ssp. pallipes | Mortality | LC50 | 30 | days | 43 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Boutet,C., and C. Chaisemartin | Specific Toxic Properties of Metallic Salts in Austro-potamobius pallipes pallipes and Orconectes limosus (Proprietes Toxiques Specifiques des sels Metalliques chez Austropotamobius pallipes pallipes et Orconectes limos | Comptes Rendus Seances Soc. Biol. Fil.167(12): 1933-1938 | 1973 | 2019/02/13 | |||||
| 甲殻類 | others Austropotamobius pallipes ssp. pallipes | Mortality | LC50 | 30 | days | 39 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Boutet,C., and C. Chaisemartin | Specific Toxic Properties of Metallic Salts in Austro-potamobius pallipes pallipes and Orconectes limosus (Proprietes Toxiques Specifiques des sels Metalliques chez Austropotamobius pallipes pallipes et Orconectes limos | Comptes Rendus Seances Soc. Biol. Fil.167(12): 1933-1938 | 1973 | 2019/02/13 | |||||
| 甲殻類 | others Orconectes limosus | Mortality | LC50 | 4 | days | 78 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Boutet,C., and C. Chaisemartin | Specific Toxic Properties of Metallic Salts in Austro-potamobius pallipes pallipes and Orconectes limosus (Proprietes Toxiques Specifiques des sels Metalliques chez Austropotamobius pallipes pallipes et Orconectes limos | Comptes Rendus Seances Soc. Biol. Fil.167(12): 1933-1938 | 1973 | 2019/02/13 | |||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | NOEC | 2.66 | days | 29 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Anderson,B.G. | The Apparent Thresholds of Toxicity to Daphnia magna for Chlorides of Various Metals when Added to Lake Erie Water | Trans. Am. Fish. Soc.78:96-113 | 1948 | 2019/02/13 | |||||
| 甲殻類 | Daphnia magna | Reproduction (Reproduction, general) | EC50 | 21 | days | 8.9 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2019/02/13 | |||||
| 甲殻類 | Daphnia magna | Intoxication (Immobile) | EC50 | 2 | days | 14.5 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12): 1691-1700 | 1972 | 2019/02/13 | |||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 14.5 | mgBa/L | 4 OECD SIDS (HPVC) | Biesinger KE and Christensen GM | Effects of Various Metals on Survival, Growth, Reproduction, and Metabolism of Daphnia magna. | J. Fis. Res. Bd. Canada, 29(12) | 1972 | 2019/02/08 | |||||||
| 甲殻類 | Daphnia magna | Basis for effect: mortality, Remarks: including immobility | LC50 | 48 | hours | 14500 | μgBa/L | × | 12 ECHA Information on Registered Substances | 2 | publication | Unnamed | 1972 | 2019/01/16 | |||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 14.5 | mg/L | 4 OECD SIDS (HPVC) | 2 | K.E. Biesinger, G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction, and Metabolism of Daphnia magna | Journal fisheries research board of Canada | 1972 | 2018/12/04 | ||||||
| 甲殻類 | Daphnia magna | Basis for effect: mortality | LC50 | 48 | hours | 19226 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1948 | 2019/01/16 | |||||
| 甲殻類 | others Austropotamobius pallipes pallipes | Basis for effect: mortality | LC50 | 96 | hours | 46000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | Boutet C and Chaisemartin C | Propriétés toxiques spécifiques des sels métalliques chez Austropotamobius pallipes pallipes et Orconectes limosus. | Société de biologie de Poitiers | 1973 | 2019/01/16 | ||||
| 甲殻類 | others Orconectes limosus | Basis for effect: mortality | LC50 | 96 | hours | 78000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | Boutet C and Chaisemartin C | Propriétés toxiques spécifiques des sels métalliques chez Austropotamobius pallipes pallipes et Orconectes limosus. | Société de biologie de Poitiers | 1973 | 2019/01/16 | ||||
| 甲殻類 | Daphnia magna | Basis for effect: mortality | LC50 | 48 | hours | 170000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | Bringmann G and Kühn R | Vergleichende wasser-toxicologische Untersuchungen an Bakterien, Algen und Kleinkrebsen | Gesundheits-Ingenieur heft 4(80) | 1959 | 2019/01/16 | ||||
| 甲殻類 | Daphnia magna | reproduction impairment | EC16 | 21 | days | 5.8 | mgBa/L | 4 OECD SIDS (HPVC) | Biesinger KE and Christensen GM | Effects of Various Metals on Survival, Growth, Reproduction, and Metabolism of Daphnia magna. | J. Fis. Res. Bd. Canada, 29(12) | 1972 | 2019/02/08 | ||||||
| 甲殻類 | Daphnia magna | reproduction impairment | EC50 | 21 | days | 8.9 | mgBa/L | 4 OECD SIDS (HPVC) | Biesinger KE and Christensen GM | Effects of Various Metals on Survival, Growth, Reproduction, and Metabolism of Daphnia magna. | J. Fis. Res. Bd. Canada, 29(12) | 1972 | 2019/02/08 | ||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 14.5 | mg/L | 10 EHC (Environmental Health Criteria) | BIESINGER, K.E. & CHRISTENSEN, G.M. | Effects of various metals on survival, growth, reproduction, and metabolism of Daphnia magna. | J. Fish Res. Board Can. | 1972 | 2019/02/27 | |||||||
| 甲殻類 | Daphnia magna | impairment | EC50 | 21 | days | 8.9 | mg/L | 10 EHC (Environmental Health Criteria) | BIESINGER, K.E. & CHRISTENSEN, G.M. | Effects of various metals on survival, growth, reproduction, and metabolism of Daphnia magna. | J. Fish Res. Board Can. | 1972 | 2019/02/27 | ||||||
| 甲殻類 | Daphnia magna | NOEL | 48 | hours | 68 | mg/L | 10 EHC (Environmental Health Criteria) | LEBLANC, G.A. | Acute toxicity of priority pollutants to water flea (Daphnia magna). | Bull. environ. Contam. Toxicol. | 1980 | 2019/02/27 | |||||||
| 甲殻類 | Daphnia magna | LC50 | 24 | hours | >530 | mg/L | 10 EHC (Environmental Health Criteria) | LEBLANC, G.A. | Acute toxicity of priority pollutants to water flea (Daphnia magna). | Bull. environ. Contam. Toxicol. | 1980 | 2019/02/27 | |||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 14.5 | mg/L | 4 OECD SIDS (HPVC) | 2 | K.E. Biesinger, G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction, and Metabolism of Daphnia magna | Journal fisheries research board of Canada | 1972 | 2018/12/04 | ||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 410 | mg/L | 10 EHC (Environmental Health Criteria) | LEBLANC, G.A. | Acute toxicity of priority pollutants to water flea (Daphnia magna). | Bull. environ. Contam. Toxicol. | 1980 | 2019/02/27 | |||||||
| 甲殻類 | Daphnia magna | LC50 | 21 | days | 13.5 | mg/L | 10 EHC (Environmental Health Criteria) | BIESINGER, K.E. & CHRISTENSEN, G.M. | Effects of various metals on survival, growth, reproduction, and metabolism of Daphnia magna. | J. Fish Res. Board Can. | 1972 | 2019/02/27 | |||||||
| 甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 | 48 | hours | 14500 | µg/L | Total | × | 16 ECOTOX | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12) | 1972 | 2022/09/15 | ||||
| 甲殻類 | Daphnia magna | Intoxication/Immobile | MATC | 96 | hours | 29 | ppm | Total | × | 16 ECOTOX | Anderson,B.G., T.F. Andrews, D.C. Chandler, and W.J. Jahoda | The Evaluation of Aquatic Invertebrates as Assay Organisms for the Determination of the Toxicity of Industrial Wastes | Final Report 51, American Petroleum Institute Project, Ohio State University, Columbus, OH | 2022/09/15 | |||||
| 甲殻類 | Daphnia magna | Intoxication/Immobile | NOEC | 16 | hours | 83 | ppm | Total | × | 16 ECOTOX | Anderson,B.G. | The Toxicity Thresholds of Various Substances Found in Industrial Wastes as Determined by the Use of Daphnia magna | Sewage Works J.16(6) | 2022/09/15 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 14500 | μg/L | nominal element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | 2022/09/15 | |||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 19226 | μg/L | nominal element | 12 ECHA Information on Registered Substances | 3 | publication | 1948 | 2022/09/15 | ||||||
| 甲殻類 | Daphnia magna | mortality | LC50 | 48 | hours | 170000 | μg/L | nominal element | 12 ECHA Information on Registered Substances | 3 | Bringmann G and Kühn R | Vergleichende wasser-toxicologische Untersuchungen an Bakterien, Algen und Kleinkrebsen | Gesundheits-Ingenieur heft 4(80) | 1959 | 2022/09/15 | ||||
| 甲殻類 | Daphnia magna | Intoxication/Immobile | NOEC | 64 | hours | 29 | ppm | Total | × | 16 ECOTOX | Anderson,B.G. | The Apparent Thresholds of Toxicity to Daphnia magna for Chlorides of Various Metals when Added to Lake Erie Water | Trans. Am. Fish. Soc.78 | 2022/09/15 | |||||
| 甲殻類 | others Caenorhabditis elegans | Basis for effect: other: survival | LOEC | 343 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 2008 | 2019/01/16 | |||||||
| 甲殻類 | others Orconectes limosus | Basis for effect: mortality | LC50 | 30 | days | 61000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | Boutet C and Chaisemartin C | Propriétés toxiques spécifiques des sels métalliques chez Austropotamobius pallipes et Orconectes limosus. | Société de biologie de poitiers, nr 167 | 1973 | 2019/01/16 | ||||
| 甲殻類 | Basis for effect: mortality | NOEC | 7 | days | 10000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 2 | publication | Unnamed | 1988 | 2019/01/16 | ||||||
| 甲殻類 | Daphnia magna | Intoxication/Immobile | EC50 | 21 | days | 13500 | µg/L | Total | × | 16 ECOTOX | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12) | 1972 | 2022/09/15 | ||||
| 甲殻類 | others Austropotamobius pallipes | Basis for effect: mortality | LC50 | 30 | days | 43000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | Boutet C and Chaisemartin C | Propriétés toxiques spécifiques des sels métalliques chez Austropotamobius pallipes et Orconectes limosus. | Société de biologie de poitiers, nr 167 | 1973 | 2019/01/16 | ||||
| 甲殻類 | others Austropotamobius pallipes | Basis for effect: mortality | LC50 | 30 | days | 39000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | Boutet C and Chaisemartin C | Propriétés toxiques spécifiques des sels métalliques chez Austropotamobius pallipes et Orconectes limosus. | Société de biologie de poitiers, nr 167 | 1973 | 2019/01/16 | ||||
| 甲殻類 | Daphnia magna | reproductive impartment | EC50 | 3 | weeks | 8.9 | mg/L | 4 OECD SIDS (HPVC) | 2 | K.E. Biesinger, G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction, and Metabolism of Daphnia magna | Journal fisheries research board of Canada | 1972 | 2018/12/04 | |||||
| 甲殻類 | Daphnia magna | Basis for effect: reproduction | EC16 | 3 | weeks | 5800 | μgBa/L | × | 12 ECHA Information on Registered Substances | 2 | publication | Unnamed | 1972 | 2019/01/16 | |||||
| 甲殻類 | Basis for effect: other: embryo hatching | NOEC | 7 | days | 10000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 2 | publication | Unnamed | 1988 | 2019/01/16 | ||||||
| 甲殻類 | others Orconectes limosus | Basis for effect: mortality | LC50 | 30 | days | 59000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | Boutet C and Chaisemartin C | Propriétés toxiques spécifiques des sels métalliques chez Austropotamobius pallipes et Orconectes limosus. | Société de biologie de poitiers, nr 167 | 1973 | 2019/01/16 | ||||
| 甲殻類 | Daphnia magna | reproductive impartment | EC50 | 3 | weeks | 8.9 | mg/L | 4 OECD SIDS (HPVC) | 2 | K.E. Biesinger, G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction, and Metabolism of Daphnia magna | Journal fisheries research board of Canada | 1972 | 2018/12/04 | |||||
| 甲殻類 | Daphnia magna | Reproduction/Reproduction, general | EC50 | 21 | days | 8900 | µg/L | Total | × | 16 ECOTOX | Biesinger,K.E., and G.M. Christensen | Effects of Various Metals on Survival, Growth, Reproduction and Metabolism of Daphnia magna | J. Fish. Res. Board Can.29(12) | 1972 | 2022/09/15 | ||||
| 甲殻類 | Daphnia magna | reproduction | EC16 | 3 | weeks | 5800 | μg/L | nominal element | × | 12 ECHA Information on Registered Substances | 2 | publication | 1972 | 2022/09/15 | |||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena pyriformis | Population (Population growth rate) | IC50 | 0.12 | days | 585 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sauvant,M.P., D. Pepin, C.A. Groliere, and J. Bohatier | Effects of Organic and Inorganic Substances on the Cell Proliferation of L-929 Fibroblasts and Tetrahymena pyriformis GL Protozoa Used for Toxicological Bioassays | Bull. Environ. Contam. Toxicol.55(2): 171-178 | 1995 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Abundance) | LOEC | 10 | days | 200 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Sex ratio) | EC50 | 10 | days | 1865 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Abundance) | LOEC | 10 | days | 302 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Abundance) | EC50 | 10 | days | 1250 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | others Oncorhynchus kisutch | Mortality | 6 | days | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | |||||||
| 魚類 | others Oncorhynchus kisutch | Mortality | 5 | days | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | |||||||
| 魚類 | others Oncorhynchus kisutch | Mortality | 3 | days | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | |||||||
| 魚類 | others Oncorhynchus kisutch | Mortality | LOEC | 3 | days | 158 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Sex ratio) | EC50 | 10 | days | 1620 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Abundance) | EC50 | 10 | days | 1057 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Development (Emergence) | ET50 | 4.65 | days | 0.000001 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Development (Pupation) | ET50 | 1.38 | days | 0.0001 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Development (Emergence) | ET50 | 4.88 | days | 0.0001 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Reproduction (Fecundity) | LOEC | days | 2000 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | ||||||
| 魚類 | others Gambusia affinis | Mortality | LC50 | 4 | days | 1640 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wallen,I.E., W.C. Greer, and R. Lasater | Toxicity to Gambusia affinis of Certain Pure Chemicals in Turbid Waters | Sewage Ind. Wastes29(6): 695-711 | 1957 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Xenopus laevis | Physiology (Conductivity) | IC50 | 0 | days | 93.7062 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Mirshahi,T. | An Investigation of the Ethanol Sensitivity of Recombinant N-Methyl-D-Aspartate Receptors Expressed in Xenopus Oocytes | Ph.D.Thesis, Virginia Commonwealth University, Richmond, VA:138 p. | 1992 | 2019/02/13 | |||||
| 魚類 | others Leuciscus idus ssp. melanotus | Mortality | LC0 | 2 | days | 450 | mg/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 | 2019/02/13 | |||||
| 魚類 | others Leuciscus idus ssp. melanotus | Mortality | LC100 | 2 | days | 955 | mg/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 | 2019/02/13 | |||||
| 魚類 | Fundulus heteroclitus (Mummichog) | Mortality | LC50 | 1 | days | >1000 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2): 21-23 | 1977 | 2019/02/13 | |||||
| 魚類 | Fundulus heteroclitus (Mummichog) | Mortality | LC50 | 3 | days | >1000 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2): 21-23 | 1977 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Sex ratio) | LOEC | 10 | days | 1003 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Lemna minor | Growth (Growth, general) | EC50 | 4 | days | 25 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wang,W. | Site-Specific Barium Toxicity to Common Duckweed, Lemna minor | Aquat. Toxicol.12(3): 203-212 | 1988 | 2019/02/13 | |||||
| 魚類 | others Gambusia affinis | Mortality | LC50 | 1 | days | 4400 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wallen,I.E., W.C. Greer, and R. Lasater | Toxicity to Gambusia affinis of Certain Pure Chemicals in Turbid Waters | Sewage Ind. Wastes29(6): 695-711 | 1957 | 2019/02/13 | |||||
| 魚類 | others Salmo trutta | Mortality | LC50 | 2 | days | 150 | mg/L | Formulation | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Woodiwiss,F.S., and G. Fretwell | The Toxicities of Sewage Effluents, Industrial Discharges and Some Chemical Substances to Brown Trout (Salmo trutta) in the Trent River Authority Area | Water Pollut. Control73:396-405 | 1974 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Development (Pupation) | ET50 | 1.46 | days | 0.000001 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | others Oncorhynchus kisutch | Mortality | NOEC | 5 | days | 158 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | |||||
| 魚類 | others Leuciscus idus ssp. melanotus | Mortality | LC50 | 2 | days | 870 | mg/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 | 2019/02/13 | |||||
| 魚類 | others Oncorhynchus kisutch | Mortality | 0.95 | days | 282 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | ||||||
| 魚類 | others Oncorhynchus kisutch | Mortality | NOEC | 3 | days | 88.8 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | |||||
| 魚類 | Fundulus heteroclitus (Mummichog) | Mortality | LC50 | 2 | days | >1000 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2): 21-23 | 1977 | 2019/02/13 | |||||
| 魚類 | others Oncorhynchus kisutch | Mortality | NOEC | 6 | days | 282 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | |||||
| 魚類 | others Oncorhynchus kisutch | Mortality | LOEC | 6 | days | 500 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | |||||
| 魚類 | Fundulus heteroclitus (Mummichog) | Mortality | LC50 | 4 | days | >1000 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2): 21-23 | 1977 | 2019/02/13 | |||||
| 魚類 | others Oncorhynchus kisutch | Mortality | LOEC | 5 | days | 282 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Holland,G.A., J.E. Lasater, E.D. Neumann, and W.E. Eldridge | Toxic Effects of Organic and Inorganic Pollutants on Young Salmon and Trout | Res. Bull. No. 5, State of Washington Dept. Fish., Seattle, WA:263 p. | 1960 | 2019/02/13 | |||||
| 魚類 | Lepomis macrochirus (Bluegill) | Reproduction (Motility) | NOEC | 0.04 | days | 520.59 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zuccarelli,M.D., and R.L. Ingermann | Calcium-Induced Quiescence of Sperm Motility in the Bluegill (Lepomis macrochirus) | J. Exp. Zool.307:590-599 | 2007 | 2019/02/13 | |||||
| 魚類 | others Gambusia affinis | Mortality | LC50 | 2 | days | 3200 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wallen,I.E., W.C. Greer, and R. Lasater | Toxicity to Gambusia affinis of Certain Pure Chemicals in Turbid Waters | Sewage Ind. Wastes29(6): 695-711 | 1957 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Mortality | LT50 | 7.05 | days | 0.01 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Development (Slowed, Retarded, Delayed or Non-development) | NOEC | days | 213 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 28 | days | 42.7 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Birge,W.J., J.A. Black, A.G. Westerman, and J.E. Hudson | Aquatic Toxicity Tests on Inorganic Elements Occurring in Oil Shale | In: C.Gale (Ed.), EPA-600/9-80-022, Oil Shale Symposium: Sampling, Analysis and Quality Assurance, March 1979, U.S.EPA, Cincinnati, OH:519-534 | 1980 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Abundance) | NOEC | 10 | days | <200 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Reproduction (Fecundity) | NOEC | 5 | days | 1283 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Mortality | LT50 | 2.57 | days | 0.1 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Sex ratio) | NOEC | 10 | days | <787 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Mortality | LT50 | 1.54 | days | 1 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Development (Pupation) | ET50 | 1.03 | days | 0.00001 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Lemna minor | Growth (Growth, general) | EC50 | 4 | days | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Wang,W. | Site-Specific Barium Toxicity to Common Duckweed, Lemna minor | Aquat. Toxicol.12(3): 203-212 | 1988 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Sex ratio) | NOEC | 10 | days | <1003 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena pyriformis | Population (Population growth rate) | IC50 | 0.37 | days | 330 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sauvant,M.P., D. Pepin, C.A. Groliere, and J. Bohatier | Effects of Organic and Inorganic Substances on the Cell Proliferation of L-929 Fibroblasts and Tetrahymena pyriformis GL Protozoa Used for Toxicological Bioassays | Bull. Environ. Contam. Toxicol.55(2): 171-178 | 1995 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena pyriformis | Population (Population growth rate) | IC50 | 0.37 | days | 350 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sauvant,M.P., D. Pepin, J. Bohatier, and C.A. Groliere | Microplate Technique for Screening and Assessing Cytotoxicity of Xenobiotics with Tetrahymena pyriformis | Ecotoxicol. Environ. Saf.32(2): 159-165 | 1995 | 2019/02/13 | |||||
| 魚類 | Lepomis macrochirus (Bluegill) | Reproduction (Motility) | NOEC | 0 | days | 520.59 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Zuccarelli,M.D., and R.L. Ingermann | Calcium-Induced Quiescence of Sperm Motility in the Bluegill (Lepomis macrochirus) | J. Exp. Zool.307:590-599 | 2007 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Development (Emergence) | ET50 | 4.03 | days | 0.00001 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Tetrahymena pyriformis | Population (Population growth rate) | IC50 | 0.25 | days | 415 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Sauvant,M.P., D. Pepin, C.A. Groliere, and J. Bohatier | Effects of Organic and Inorganic Substances on the Cell Proliferation of L-929 Fibroblasts and Tetrahymena pyriformis GL Protozoa Used for Toxicological Bioassays | Bull. Environ. Contam. Toxicol.55(2): 171-178 | 1995 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Development (Slowed, Retarded, Delayed or Non-development) | LOEC | days | 1283 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Reproduction (Fecundity) | NOEC | days | 400 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | ||||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Abundance) | NOEC | 10 | days | <302 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Reproduction (Fecundity) | LOEC | 5 | days | 4109 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Culex pipiens ssp. pallens | Mortality | LT50 | 6.98 | days | 0.001 | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Suzuki,K. | The Toxic Influence of Heavy Metal Salts upon Mosquito Larvae | J. Fac. Sci. Hokkaido Univ.6(14): 196-209 | 1959 | 2019/02/13 | ||||||
| 魚類 | Fundulus heteroclitus (Mummichog) | Mortality | LC50 | 4 | days | >1000 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2): 21-23 | 1977 | 2019/02/13 | |||||
| 魚類 | Fundulus heteroclitus (Mummichog) | Mortality | LC50 | 1 | days | >1000 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2): 21-23 | 1977 | 2019/02/13 | |||||
| 魚類 | Fundulus heteroclitus (Mummichog) | Mortality | LC50 | 2 | days | >1000 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2): 21-23 | 1977 | 2019/02/13 | |||||
| 魚類 | Fundulus heteroclitus (Mummichog) | Mortality | LC50 | 3 | days | >1000 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2): 21-23 | 1977 | 2019/02/13 | |||||
| 魚類 | Poecilia reticulata (Guppy) Pellioditis marina | Population (Sex ratio) | LOEC | 10 | days | 787 | mg/L | Total | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Lira,V.F., G.A.P. Santos, S. Derycke, M.E.L. Larrazabal, V.G. Fonseca-Genevois, and T. Moens | Effects of Barium and Cadmium on the Population Development of the Marine Nematode Rhabditis (Pellioditis) marina | Mar. Environ. Res.72(4): 151-159 | 2011 | 2019/02/13 | |||||
| 魚類 | Oncorhynchus mykiss | Mortality/Mortality | LC50 | 28 | days | 42700 | µg/L | Total | × | 16 ECOTOX | Birge,W.J., J.A. Black, A.G. Westerman, and J.E. Hudson | Aquatic Toxicity Tests on Inorganic Elements Occurring in Oil Shale | In: C.Gale (Ed.), EPA-600/9-80-022, Oil Shale Symposium: Sampling, Analysis and Quality Assurance, March 1979, U.S.EPA, Cincinnati, OH | 1980 | 2022/09/15 | ||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 72 | hours | >1000 | mg/L | 4 OECD SIDS (HPVC) | 2 | D. Dorfman | Tolerance of Fundulus Heteroclitus to Different Metals in Salt Waters | Bull. New Jersey Acad.Sci | 1977 | 2018/12/04 | ||||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 96 | hours | >1000 | mgBa/L | 4 OECD SIDS (HPVC) | Dorfman D | Tolerance of Fundulus Heteroclitus to Different Metals in Salt Waters. | Bull. New Jersey Acad.Sci., 22(2) | 1977 | 2019/02/08 | |||||||
| 魚類 | others Gambusia affinis | Basis for effect: mortality | 24 | hours | 4400000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1957 | 2019/01/16 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Basis for effect: mortality | LC50 | 96 | hours | >3.5 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 48 | hours | >1000 | mg/L | 4 OECD SIDS (HPVC) | 2 | D. Dorfman | Tolerance of Fundulus Heteroclitus to Different Metals in Salt Waters | Bull. New Jersey Acad.Sci | 1977 | 2018/12/04 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Basis for effect: mortality | LC50 | 96 | hours | >174 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 魚類 | others Gambusia affinis | Basis for effect: mortality | 96 | hours | 1640000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1957 | 2019/01/16 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Basis for effect: mortality | LC50 | 96 | hours | >97.5 | mgBa/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2010 | 2019/01/16 | |||||
| 魚類 | Pimephales promelas (Fathead minnow) | Basis for effect: other: neutral red uptake method | NI50 | 2 | hours | 604000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1992 | 2019/01/16 | |||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 96 | hours | >1000 | mg/L | 4 OECD SIDS (HPVC) | 2 | D. Dorfman | Tolerance of Fundulus Heteroclitus to Different Metals in Salt Waters | Bull. New Jersey Acad.Sci | 1977 | 2018/12/04 | ||||||
| 魚類 | Fundulus heteroclitus (Mummichog) | Basis for effect: mortality | TL50 | 96 | hours | >1000000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | Dorfman D | Tolerance of Fundulus heteroclitus to different metals in salt waters. | Bulletin of the New Jersey Academy of Science, nr 22 | 1977 | 2019/01/16 | ||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 24 | hours | >1000 | mg/L | 4 OECD SIDS (HPVC) | 2 | D. Dorfman | Tolerance of Fundulus Heteroclitus to Different Metals in Salt Waters | Bull. New Jersey Acad.Sci | 1977 | 2018/12/04 | ||||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 72 | hours | >1000 | mg/L | 4 OECD SIDS (HPVC) | 2 | D. Dorfman | Tolerance of Fundulus Heteroclitus to Different Metals in Salt Waters | Bull. New Jersey Acad.Sci | 1977 | 2018/12/04 | ||||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 48 | hours | >1000 | mg/L | 4 OECD SIDS (HPVC) | 2 | D. Dorfman | Tolerance of Fundulus Heteroclitus to Different Metals in Salt Waters | Bull. New Jersey Acad.Sci | 1977 | 2018/12/04 | ||||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 96 | hours | >1000 | mg/L | 4 OECD SIDS (HPVC) | 2 | D. Dorfman | Tolerance of Fundulus Heteroclitus to Different Metals in Salt Waters | Bull. New Jersey Acad.Sci | 1977 | 2018/12/04 | ||||||
| 魚類 | Fundulus heteroclitus (Mummichog) | LC50 | 24 | hours | >1000 | mg/L | 4 OECD SIDS (HPVC) | 2 | D. Dorfman | Tolerance of Fundulus Heteroclitus to Different Metals in Salt Waters | Bull. New Jersey Acad.Sci | 1977 | 2018/12/04 | ||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | impairment | EC50 | 96 | hours | >500 | mg/L | 10 EHC (Environmental Health Criteria) | HEITMULLER, P.T., HOLLISTER, T.A., & PARRISH, P.R. | Acute toxicity of 54 industrial chemicals to sheepshead minnows (Cyprinodon variegatus). | Bull. Environ. Contam. Toxicol. | 1981 | 2019/02/27 | ||||||
| 魚類 | Fundulus heteroclitus | Mortality/Mortality | LC50 | 48 | hours | >1000000 | µg/L | Total | × | 16 ECOTOX | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | 2022/09/15 | ||||
| 魚類 | Pimephales promelas | neutral red uptake method | NI50 | 2 | hours | 604000 | μg/L | not specified element | 12 ECHA Information on Registered Substances | 3 | publication | 1992 | 2022/09/15 | ||||||
| 魚類 | Danio rerio | mortality (fish) | LC50 | 96 | hours | >3.5 | mg/L | meas. (geom. mean) dissolved | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 魚類 | Fundulus heteroclitus | Mortality/Mortality | LC50 | 48 | hours | >1000000 | µg/L | Total | × | 16 ECOTOX | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | 2022/09/15 | ||||
| 魚類 | Fundulus heteroclitus | Mortality/Mortality | LC50 | 96 | hours | >1000000 | µg/L | Total | × | 16 ECOTOX | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | 2022/09/15 | ||||
| 魚類 | Fundulus heteroclitus | Mortality/Mortality | LC50 | 72 | hours | >1000000 | µg/L | Total | × | 16 ECOTOX | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | 2022/09/15 | ||||
| 魚類 | Fundulus heteroclitus | Mortality/Mortality | LC50 | 24 | hours | >1000000 | µg/L | Total | × | 16 ECOTOX | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | 2022/09/15 | ||||
| 魚類 | Fundulus heteroclitus | Mortality/Mortality | LC50 | 96 | hours | >1000000 | µg/L | Total | × | 16 ECOTOX | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | 2022/09/15 | ||||
| 魚類 | Fundulus heteroclitus | Mortality/Mortality | LC50 | 24 | hours | >1000000 | µg/L | Total | × | 16 ECOTOX | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | 2022/09/15 | ||||
| 魚類 | Danio rerio | mortality (fish) | LC50 | 96 | hours | >97.5 | mg/L | meas. (geom. mean) element | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 魚類 | Fundulus heteroclitus | mortality | TL50 | 96 | hours | >1000000 | μg/L | not specified element | 12 ECHA Information on Registered Substances | 3 | Dorfman D | Tolerance of Fundulus heteroclitus to different metals in salt waters. | Bulletin of the New Jersey Academy of Science, nr 22, pg 21-23 | 1977 | 2022/09/15 | ||||
| 魚類 | Leuciscus idus melanotus | mortality | LC100 | 955000 | μg/L | not specified element | ○ | 12 ECHA Information on Registered Substances | 3 | Juhnke VI and Lüdemann D | Ergebnisse der Untersuching von 200 chemische Verbindungen auf acute Fischtoxizität mit dem Goldorfentest | Eingegangen 14, nr8 | 1978 | 2022/09/15 | |||||
| 魚類 | Leuciscus idus melanotus | mortality | LC50 | 870000 | not specified element | ○ | 12 ECHA Information on Registered Substances | 3 | Juhnke VI and Lüdemann D | Ergebnisse der Untersuching von 200 chemische Verbindungen auf acute Fischtoxizität mit dem Goldorfentest | Eingegangen 14, nr8 | 1978 | 2022/09/15 | ||||||
| 魚類 | Leuciscus idus melanotus | mortality | LC0 | 450000 | not specified element | ○ | 12 ECHA Information on Registered Substances | 3 | Juhnke VI and Lüdemann D | Ergebnisse der Untersuching von 200 chemische Verbindungen auf acute Fischtoxizität mit dem Goldorfentest | Eingegangen 14, nr8 | 1978 | 2022/09/15 | ||||||
| 魚類 | Danio rerio | mortality | LC50 | 96 | hours | >174 | mg/L | meas. (geom. mean) test mat. | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2010 | 2022/09/15 | ||||
| 魚類 | Fundulus heteroclitus | Mortality/Mortality | LC50 | 72 | hours | >1000000 | µg/L | Total | × | 16 ECOTOX | Dorfman,D. | Tolerance of Fundulus heteroclitus to Different Metals in Salt Waters | Bull. N. J. Acad. Sci.22(2) | 1977 | 2022/09/15 | ||||
| 魚類 | Lepomis macrochirus | Reproduction/Motility | NOEC | 0 | minutes | 2.5 | mmol/L | Total | × | 16 ECOTOX | Zuccarelli,M.D., and R.L. Ingermann | Calcium-Induced Quiescence of Sperm Motility in the Bluegill (Lepomis macrochirus) | J. Exp. Zool.307 | 2022/09/15 | |||||
| 魚類 | Lepomis macrochirus | Reproduction/Motility | NOEC | 60 | minutes | 2.5 | mmol/L | Total | × | 16 ECOTOX | Zuccarelli,M.D., and R.L. Ingermann | Calcium-Induced Quiescence of Sperm Motility in the Bluegill (Lepomis macrochirus) | J. Exp. Zool.307 | 2022/09/15 | |||||
| 魚類 | others Gambusia affinis | Basis for effect: mortality | 48 | hours | 3200000 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1957 | 2019/01/16 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Basis for effect: other: hatching success, mortality (post-hatch success), numbers of healthy fish, length of the surviving fish, dry weight of the surviving fish | LOEC | 33 | days | >100 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2014 | 2019/01/16 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Basis for effect: mortality, Remarks: mortality and teratogenesis | LC1 | 28 | days | 2813 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1980 | 2019/01/16 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Basis for effect: mortality, Remarks: mortality and teratogenesis | LC50 | 28 | days | 42700 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1980 | 2019/01/16 | |||||
| 魚類 | Danio rerio (Zebrafish) | Basis for effect: other: hatching success, mortality (post-hatch success), numbers of healthy fish, length of the surviving fish, dry weight of the surviving sh | NOEC | 33 | days | >=100 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2014 | 2019/01/16 | |||||
| 魚類 | Danio rerio (Zebrafish) | Basis for effect: other: hatching success, mortality (post-hatch success), numbers of healthy fish, length of the surviving fish, dry weight of the surviving fish | LOEC | 33 | days | >40.3 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2014 | 2019/01/16 | |||||
| 魚類 | Danio rerio (Zebrafish) | NOEC | 33 | days | >=1.26 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2014 | 2019/01/16 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Basis for effect: mortality, Remarks: mortality and teratogenesis | LC10 | 28 | days | 9543 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1980 | 2019/01/16 | |||||
| 魚類 | Danio rerio (Zebrafish) | LOEC | 33 | days | >1.26 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2014 | 2019/01/16 | ||||||
| 魚類 | Danio rerio (Zebrafish) | Basis for effect: other: hatching success, mortality (post-hatch success), numbers of healthy fish, length of the surviving fish, dry weight of the surviving sh | NOEC | 33 | days | >=40.3 | mg/L | ○ | 12 ECHA Information on Registered Substances | 1 | study report | Unnamed | 2014 | 2019/01/16 | |||||
| 魚類 | Danio rerio | LOEC | 33 | days | >1.26 | mg/L | meas. (geom. mean) dissolved | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2014 | 2022/09/15 | |||||
| 魚類 | Danio rerio | NOEC | 33 | days | >=1.26 | mg/L | meas. (geom. mean) dissolved | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2014 | 2022/09/15 | |||||
| 魚類 | Oncorhynchus mykiss | mortality | LC50 | 28 | days | 42700 | μg/L | meas. (not specified) element | 12 ECHA Information on Registered Substances | 3 | publication | 1980 | 2022/09/15 | ||||||
| 魚類 | Oncorhynchus mykiss | mortality | LC1 | 28 | days | 2813 | μg/L | meas. (not specified) element | 12 ECHA Information on Registered Substances | 3 | publication | 1980 | 2022/09/15 | ||||||
| 魚類 | Danio rerio | hatching success, mortality (post-hatch suc | NOEC | 33 | days | >=100 | mg/L | nominal test mat. | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2014 | 2022/09/15 | ||||
| 魚類 | Danio rerio | hatching success, mortality (post-hatch suc | LOEC | 33 | days | >40.3 | mg/L | meas. (geom. mean) total barium | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2014 | 2022/09/15 | ||||
| 魚類 | Danio rerio | hatching success, mortality (post-hatch suc | LOEC | 33 | days | >100 | mg/L | nominal test mat. | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2014 | 2022/09/15 | ||||
| 魚類 | Oncorhynchus mykiss | mortality | LC10 | 28 | days | 9543 | μg/L | meas. (not specified) element | 12 ECHA Information on Registered Substances | 3 | publication | 1980 | 2022/09/15 | ||||||
| 魚類 | Danio rerio | hatching success, mortality (post-hatch suc | NOEC | 33 | days | >=40.3 | mg/L | meas. (geom. mean) total barium | ○ | ○ | 12 ECHA Information on Registered Substances | 1 | study report | 2014 | 2022/09/15 | ||||
| その他 | Spongilla lacustris | Basis for effect: other: germination | LOEC | 72 | hours | <137327 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1978 | 2019/01/16 | |||||
| その他 | Spongilla lacustris | Basis for effect: other: hatching | LOEC | 72 | hours | 137327 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1978 | 2019/01/16 | |||||
| その他 | Lemna minor | EC50 | 96 | hours | 61 | mg/L | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | ||||||
| その他 | Lemna minor | IC50 | 96 | hours | 113～149 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | >400 | mg/L | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | ||||||
| その他 | Spongilla lacustris | Basis for effect: other: hatching | NOEC | 72 | hours | 13733 | μgBa/L | × | 12 ECHA Information on Registered Substances | 3 | publication | Unnamed | 1978 | 2019/01/16 | |||||
| その他 | Lemna minor | IC50 | 96 | hours | 331～>400 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 52～173 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 330～>400 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | growth rate | EC50 | 96 | hours | 26 | mg/L | 4 OECD SIDS (HPVC) | 2 | W. Wang | The Effect of River water on Phytotoxicity of Ba, Cd, and Cr | Environmental Pollution (Series B) | 1986 | 2018/12/04 | |||||
| その他 | Lemna minor | IC50 | 96 | hours | 143～194 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 113～156 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 280～>400 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 310～>400 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 328～372 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 152～245 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 61～143 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 300～328 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 58～155 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 220～345 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 73～130 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 104～135 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 155～337 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 73～130 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 328～372 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 330～>400 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 113～149 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 155～337 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 143～194 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 331～>400 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 58～155 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 300～328 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 310～>400 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 280～>400 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 61～143 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | growth rate | EC50 | 96 | hours | 26 | mg/L | 4 OECD SIDS (HPVC) | 2 | W. Wang | The Effect of River water on Phytotoxicity of Ba, Cd, and Cr | Environmental Pollution (Series B) | 1986 | 2018/12/04 | |||||
| その他 | Lemna minor | EC50 | 96 | hours | 61 | mg/L | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | ||||||
| その他 | Lemna minor | IC50 | 96 | hours | 104～135 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | >400 | mg/L | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | ||||||
| その他 | Lemna minor | IC50 | 96 | hours | 52～173 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 113～156 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 220～345 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 | |||||||
| その他 | Lemna minor | IC50 | 96 | hours | 152～245 | 4 OECD SIDS (HPVC) | 2 | W. Wang | Site-specific barium toxicity to common duckweed, Lemna minor | Aquatic Toxicology | 1988 | 2018/12/04 |