【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 | Pseudokirchneriella subcapitata | EC50 | 96 | hours | >6100 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 藻類 | Skeletonema costatum | EC50 | 96 | hours | >4580 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 藻類 | Navicula pelliculosa | EC50 | 96 | hours | >7400 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/11/27 | ||||||||||
| 藻類 | Anabaena flos-aquae | EC50 | 96 | hours | >6110 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/11/27 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | EC50 | 72 | hours | >32700 | ppb | 3 USEPA Pesticide Ecotoxicity Database | IN | 2019/12/04 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth rate | EC50 | 3 | days | >2700 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | B | U.S. EPA | US EPA HPV Chemical Challenge Program, Robust Summaries for Carbamic Acid, 1H-Benzimidazol-2-YL-, Methyl Ester (CAS No. 10605-21-7). | 2005 | 2020/02/18 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | cell number | EC50 | 72 | hours | 2.4 | mg/L | ○ | 1, 2, 4, 8, 16 mg-Carbendazim125g/L | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||
| 藻類 | Chlorella pyrenoidosa | Growth | EC50 | 2 | days | 340 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | D | Canton, J.H. | The Toxicity of Benomyl, Thiophanate-Methyl, and BCM to Four Freshwater Organisms. | Bull.Environ.Contam.Toxicol. 16(2) | 1976 | 2020/02/18 | |||||
| 藻類 | Biomass | EC50 | 72 | hours | 7.7 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | EFSA | Conclusion on the peer review of the pesticide risk assessment of the active substance carbendazim | http://dx.doi.org/10.2903/j.efsa.2010.1598 | 2010 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 2.6 | mg/L | ○ | 1, 2, 4, 8, 16 mg-Carbendazim125g/L | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||
| 藻類 | Desmodesmus subspicatus | growth rate | EC50 | 72 | hours | 419 | mg/L | ○ | 0, 1.0, 1.8, 3.2, 5.6, 10, 18, 32, 56, 100, 180, 320, 560, 1000 mg | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 1.3 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | EC50 | 72 | hours | 7.7 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | |||||||
| 藻類 | Chlorella pyrenoidosa | PopulationPopulation growth rate | EC50 EC50 | 96 | hours | 34.6575 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ma,J., R. Zheng, L. Xu, and S. Wang | Differential Sensitivity of Two Green Algae, Scenedesmus obliqnus and Chlorella pyrenoidosa, to 12 Pesticides | Ecotoxicol. Environ. Saf.52(1) | 2002 | |||||||
| 藻類 | Chlorella pyrenoidosa | GrowthGrowth, general | EC50 EC50 | 48 | hours | 340 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H. | The Toxicity of Benomyl, Thiophanate-Methyl, and BCM to Four Freshwater Organisms | Bull. Environ. Contam. Toxicol.16(2) | 1976 | |||||||
| 藻類 | Scenedesmus acutus var. acutus | PopulationPopulation growth rate | EC50 EC50 | 96 | hours | 19.0562 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ma,J., R. Zheng, L. Xu, and S. Wang | Differential Sensitivity of Two Green Algae, Scenedesmus obliqnus and Chlorella pyrenoidosa, to 12 Pesticides | Ecotoxicol. Environ. Saf.52(1) | 2002 | |||||||
| 藻類 | Navicula pelliculosa | NOEL | 96 | hours | 7400 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | NOEL | 96 | hours | 2100 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 藻類 | Pseudokirchneriella subcapitata | NOEL | 72 | hours | 360 | ppb | 3 USEPA Pesticide Ecotoxicity Database | IN | 2019/12/04 | ||||||||||
| 藻類 | Skeletonema costatum | NOEL | 96 | hours | 4580 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 藻類 | Anabaena flos-aquae | NOEL | 96 | hours | 6110 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/12/04 | ||||||||||
| 藻類 | Desmodesmus subspicatus | NOEC | 72 | hours | 10 | mg/L | ○ | 0, 1.0, 1.8, 3.2, 5.6, 10, 18, 32, 56, 100, 180, 320, 560, 1000 mg | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | NOEC | 72 | hours | 2.5 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | |||||||
| 藻類 | Pseudokirchneriella subcapitata | NOEC | 72 | hours | 0.5 | mg/L | × | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||||
| 藻類 | Pseudokirchneriella subcapitata | biomass | NOEC | 72 | hours | 1 | mg/L | ○ | 1, 2, 4, 8, 16 mg-Carbendazim125g/L | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | growth rate | NOEC | 72 | hours | 2 | mg/L | ○ | 1, 2, 4, 8, 16 mg-Carbendazim125g/L | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||
| 藻類 | Pseudokirchneriella subcapitata | Growth rate | NOEC | 3 | days | 1000 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | B | U.S. EPA | US EPA HPV Chemical Challenge Program, Robust Summaries for Carbamic Acid, 1H-Benzimidazol-2-YL-, Methyl Ester (CAS No. 10605-21-7). | 2005 | 2020/02/18 | ||||||
| 藻類 | Scenedesmus acutus | PopulationAbundance | NOEC NOEC | 4 | weeks | 330 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van den Brink,P.J., J. Hattink, F. Bransen, E. Van Donk, and T.C.M. Brock | Impact of the Fungicide Carbendazim in Freshwater Microcosms. II. Zooplankton, Primary Producers and Final Conclusions | Aquat. Toxicol.48(2-3) | 2000 | |||||||
| 藻類 | Anabaena azollae | PhysiologyAmmonia excretion | LOEC LOEC | 60 | hours | 4.8 | ppm [Active ingredient] | 0 ppm / 4.8 ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Uma,D., and S. Kannaiyan | Effect of the Systemic Fungicide, Bavistin on the Nitrogen Status of Cyanobacteria Under Immobilized State in Polyurethane Foam | S. Afr. J. Bot.62(3) | 1996 | ||||||
| 藻類 | Anabaena azollae | PhysiologyAmmonia excretion | NOEC NOEC | 60 | hours | 4.8 | ppm [Active ingredient] | 0 ppm / 4.8 ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Uma,D., and S. Kannaiyan | Effect of the Systemic Fungicide, Bavistin on the Nitrogen Status of Cyanobacteria Under Immobilized State in Polyurethane Foam | S. Afr. J. Bot.62(3) | 1996 | ||||||
| 藻類 | Anabaena variabilis | PopulationAbundance | NOEC NOEC | 60 | hours | 4.8 | ppm [Active ingredient] | 0 ppm / 4.8 ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Uma,D., and S. Kannaiyan | Effect of the Systemic Fungicide, Bavistin on the Nitrogen Status of Cyanobacteria Under Immobilized State in Polyurethane Foam | S. Afr. J. Bot.62(3) | 1996 | ||||||
| 藻類 | Anabaena variabilis | PhysiologyAmmonia excretion | LOEC LOEC | 60 | hours | 4.8 | ppm [Active ingredient] | 0 ppm / 4.8 ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Uma,D., and S. Kannaiyan | Effect of the Systemic Fungicide, Bavistin on the Nitrogen Status of Cyanobacteria Under Immobilized State in Polyurethane Foam | S. Afr. J. Bot.62(3) | 1996 | ||||||
| 藻類 | Scenedesmus acutus | PopulationAbundance | LOEC LOEC | 4 | weeks | 1000 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van den Brink,P.J., J. Hattink, F. Bransen, E. Van Donk, and T.C.M. Brock | Impact of the Fungicide Carbendazim in Freshwater Microcosms. II. Zooplankton, Primary Producers and Final Conclusions | Aquat. Toxicol.48(2-3) | 2000 | |||||||
| 藻類 | Anabaena variabilis | PopulationAbundance | LOEC LOEC | 60 | hours | 4.8 | ppm [Active ingredient] | 0 ppm / 4.8 ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Uma,D., and S. Kannaiyan | Effect of the Systemic Fungicide, Bavistin on the Nitrogen Status of Cyanobacteria Under Immobilized State in Polyurethane Foam | S. Afr. J. Bot.62(3) | 1996 | ||||||
| 藻類 | Anabaena variabilis | PhysiologyAmmonia excretion | LOEC LOEC | 60 | hours | 4.8 | ppm [Active ingredient] | 0 ppm / 4.8 ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Uma,D., and S. Kannaiyan | Effect of the Systemic Fungicide, Bavistin on the Nitrogen Status of Cyanobacteria Under Immobilized State in Polyurethane Foam | S. Afr. J. Bot.62(3) | 1996 | ||||||
| 藻類 | Anabaena azollae | PopulationAbundance | LOEC LOEC | 60 | hours | 4.8 | ppm [Active ingredient] | 0 ppm / 4.8 ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Uma,D., and S. Kannaiyan | Effect of the Systemic Fungicide, Bavistin on the Nitrogen Status of Cyanobacteria Under Immobilized State in Polyurethane Foam | S. Afr. J. Bot.62(3) | 1996 | ||||||
| 藻類 | Anabaena azollae | PopulationAbundance | LOEC LOEC | 60 | hours | 4.8 | ppm [Active ingredient] | 0 ppm / 4.8 ppm | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Uma,D., and S. Kannaiyan | Effect of the Systemic Fungicide, Bavistin on the Nitrogen Status of Cyanobacteria Under Immobilized State in Polyurethane Foam | S. Afr. J. Bot.62(3) | 1996 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 96 | hours | 186 | μg/L [Formulation] | 0 ug/L / 2.2-2550 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC10 LC10 | 7 | days | 32 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC10 LC10 | 96 | hours | 53 | μg/L [Formulation] | 0 ug/L / 2.2-2550 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC10 LC10 | 96 | hours | 35 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | days | >100～<200 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 50-450 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | |||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 7 | days | 61 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 96 | hours | 399 | μg/L [Formulation] | 0 ug/L / 2.2-2550 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | days | 55 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 7 | days | 61 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 7 | days | 62 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 7 | days | >150 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 7 | days | >150 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 7 | days | >150 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | days | >450 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 50-450 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | |||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | days | >150～<200 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 50-450 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | |||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 96 | hours | 87 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC10 EC10 | 96 | hours | 68 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC10 EC10 | 96 | hours | 56 | μg/L [Formulation] | 0 ug/L / 2.2-2550 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 96 | hours | 91 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC10 EC10 | 7 | days | 32 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC10 EC10 | days | 32 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | |||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | days | >300～<400 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 50-450 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | |||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC10 EC10 | 7 | days | 15 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van den Brink,P.J., J. Hattink, F. Bransen, E. Van Donk, and T.C.M. Brock | Impact of the Fungicide Carbendazim in Freshwater Microcosms. II. Zooplankton, Primary Producers and Final Conclusions | Aquat. Toxicol.48(2-3) | 2000 | |||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 0.46 | mg/L | 10 EHC (Environmental Health Criteria) | Canton JH | The toxicity of benomyl, thiophanate-methyl, and BLM to four freshwater organisms. | Bull Environ Contam Toxicol, 16 | 1976 | 2019/12/18 | |||||||
| 甲殻類 | Americamysis bahia | LC50 | 96 | hours | 98 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/11/27 | ||||||||||
| 甲殻類 | Americamysis bahia | NOEL | 96 | hours | 33 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 甲殻類 | Daphnia magna | LC50 | 48 | hours | 0.087 | mg/L | 10 EHC (Environmental Health Criteria) | Hutton DG | Static acute 48-hours EC50 of carbamic acid, 1H-benzimidazol-2-yl-, methyl ester to fed Daphnia magna. | Newark, Delaware, E.I. Du Pont de Nemours and Co., Inc., Haskell Laboratory (Unpublished report No.HLR 638-88) | 1988 | 2019/12/18 | |||||||
| 甲殻類 | Daphnia magna | NOEL | 48 | hours | 130 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 390 | ppb | 3 USEPA Pesticide Ecotoxicity Database | 2019/11/27 | |||||||||||
| 甲殻類 | Mysidopsis bahia | LC50 | 96 | hours | 0.098 | mg/L | 10 EHC (Environmental Health Criteria) | Boeri RL | Static acute toxicity of carbendazim technical to the mysid, Mysidopsis bahia. | Marblehead, Massachusetts, Enseco (Unpublished report No. HLO 829-88, prepared for E.I. Du Pont de Nemours and Co., Inc.) | 1988 | 2019/12/18 | |||||||
| 甲殻類 | Daphnia magna | NOEL | 48 | hours | 110 | ppb | 3 USEPA Pesticide Ecotoxicity Database | 2019/12/04 | |||||||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 350 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/11/27 | ||||||||||
| 甲殻類 | Daphnia magna | EC50 | 48 | hours | 110 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/12/04 | ||||||||||
| 甲殻類 | Crassostrea virginica | rate of shell deposition | EC50 | 96 | hours | >1.145 | mg/L | 10 EHC (Environmental Health Criteria) | Boeri RL | Flow through acute toxicity of carbendazim technical to the eastern oyster, Crassostrea virginica. | Marblehead, Massachusetts, Enseco (Unpublished report No. HLO 15-89, prepared for E.I. Du Pont de Nemours and Co., Inc.) | 1988 | 2019/12/18 | ||||||
| 甲殻類 | Crassostrea virginica | NOEL | 96 | hours | 1145 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 甲殻類 | Crassostrea virginica | EC50 | 96 | hours | >1145 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/11/29 | ||||||||||
| 甲殻類 | Daphnia magna | Mortality | LC50 | 2 | days | 460 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | D | Canton, J.H. | The Toxicity of Benomyl, Thiophanate-Methyl, and BCM to Four Freshwater Organisms. | Bull.Environ.Contam.Toxicol. 16(2) | 1976 | 2020/02/18 | |||||
| 甲殻類 | Daphnia magna | NOEC | 48 | hours | 0.043 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 2 | days | 160 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | A | U.S. EPA | US EPA HPV Chemical Challenge Program, Robust Summaries for Carbamic Acid, 1H-Benzimidazol-2-YL-, Methyl Ester (CAS No. 10605-21-7). | 2005 | 2020/02/18 | ||||||
| 甲殻類 | Daphnia magna | Immobilization | EC50 | 2 | days | 160 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | B | Ferreira, A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna. | Aquat.Toxicol. 89 | 2008 | 2020/02/18 | |||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.19 | mg/L | ○ | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | |||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.39 | mg/L | ○ | 0, 0.084, 0.12, 0.17, 0.25, 0.35, 0.50 mg/L | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.35 | mg/L | × | 0.13 - 1.25 mg/L | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||
| 甲殻類 | Daphnia magna | mobility | EC50 | 48 | hours | 0.15 | mg/L | ○ | 0.0010-1000 mg/L (25濃度区） | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||
| 甲殻類 | Mortality | LC50 | 48 | hours | 0.00288 | mmol/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | Peter C. von der Ohe, Ralph Kühne, Ralf-Uwe Ebert, Rolf Altenburger, Matthias Liess, and Gerrit Schüürmann | Structural Alerts-A New Classification Model to Discriminate Excess Toxicity from Narcotic Effect Levels of Organic Compounds in the Acute Daphnid Assay | Chem. Res. Toxicol., 18 (3) | 2005 | ||||||||
| 甲殻類 | Daphnia magna | mobility | NOEC | 48 | hours | 0.11 | mg/L | ○ | 0, 0.084, 0.12, 0.17, 0.25, 0.35, 0.50 mg/L | 12 ECHA Information on Registered Substances | 2 | publication | 2009 | ||||||
| 甲殻類 | Mortality | EC50 | 48 | hours | 0.15 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | EFSA | Conclusion on the peer review of the pesticide risk assessment of the active substance carbendazim | http://dx.doi.org/10.2903/j.efsa.2010.1598 | 2010 | ||||||||
| 甲殻類 | Americamysis bahia | MortalityMortality | NOEL NOEL | 96 | hours | 33 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | NOEL NOEL | 48 | hours | 130 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 48 | hours | 87.6 | μg/L [Active ingredient] | 0 ug/L / 40 ug/L / 60 ug/L / 80 ug/L / 100 ug/L / 120 ug/L / 140 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | NR-ZERO | 24 | hours | 100 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | NR-ZERO | 24 | hours | 100 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | NOEC NOEC | 28 | hours | <100 | μg/L [Active ingredient] | 0 ug/L / 100 ug/L / 165 ug/L / 230 ug/L / 295 ug/L / 360 ug/L / 425 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 48 | hours | 1336 | μg/L [Formulation] | 0 ug/L / 2.2-2550 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | NOEC NOEC | 24 | hours | 60 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | NR-ZERO | 24 | hours | 100 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC10 LC10 | 48 | hours | 224 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | NR-ZERO | 24 | hours | 100 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 30 | hours | 85.35 | μg/L [Active ingredient] | 0 ug/L / 12.5-100 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 26 | hours | 164.33 | μg/L [Active ingredient] | 0 ug/L / 12.5-100 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 48 | hours | 110 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | EC50 EC50 | 24 | hours | 28.6 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | NOEC NOEC | 24 | hours | 230 | μg/L [Active ingredient] | 0 ug/L / 100 ug/L / 165 ug/L / 230 ug/L / 295 ug/L / 360 ug/L / 425 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >150～<200 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Americamysis bahia | MortalityMortality | LC50 LC50 | 96 | hours | 98 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia pulex | MortalityMortality | LC50 LC50 | 48 | hours | 26.1 | μg/L [Formulation] | 0 ug/L / 2.30 ug/L / 4.90 ug/L / 9.70 ug/L / 19.40 ug/L / 38.80 ug/L / 77.70 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Encina,F., P.D.L.R. Escalante, and K. Salazar | Acute Toxicity (LC50) of a Pesticide (Carbendazim) on Two Native Crustacean Zooplankton Species: Daphnia pulex Leydig, 1860 and Tumeodiaptomus diabolicus (Brehm, 1935) from Northern Patagonian Lakes (Chile) | Crustaceana (Leiden)90(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 100 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 28.2 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | NR-ZERO | 24 | hours | 100 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 320 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | NR-ZERO | 48 | hours | 2 | mM [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Pattanasupong,A., H. Nagase, E. Sugimoto, Y. Hori, K. Hirata, K. Tani, M. Nasu, and K. Miyamoto | Degradation of Carbendazim and 2,4-Dichlorophenoxyacetic Acid by Immobilized Consortium on Loofa Sponge | J. Biosci. Bioeng.98(1) | 2004 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 100 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC10 LC10 | 48 | hours | >8000 | μg/L [Formulation] | 0 ug/L / 2.2-2550 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | LOEC LOEC | 24 | hours | 295 | μg/L [Active ingredient] | 0 ug/L / 100 ug/L / 165 ug/L / 230 ug/L / 295 ug/L / 360 ug/L / 425 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | LOEC LOEC | 28 | hours | 100 | μg/L [Active ingredient] | 0 ug/L / 100 ug/L / 165 ug/L / 230 ug/L / 295 ug/L / 360 ug/L / 425 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | LOEC LOEC | 24 | hours | 70 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Crassostrea virginica | IntoxicationImmobile | NOEL NOEL | 96 | hours | >1145 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Crassostrea virginica | IntoxicationImmobile | EC50 EC50 | 96 | hours | >1160 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | NR-ZERO | 24 | hours | 100 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 54.1 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 29 | hours | 165.38 | μg/L [Active ingredient] | 0 ug/L / 12.5-100 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 24 | hours | 3.5 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 48 | hours | 192 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | EC50 EC50 | 24 | hours | 97.54 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | EC50 EC50 | 24 | hours | 24.4 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 24 | hours | 325.6 | μg/L [Active ingredient] | 0 ug/L / 100 ug/L / 165 ug/L / 230 ug/L / 295 ug/L / 360 ug/L / 425 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 28 | hours | 115.86 | μg/L [Active ingredient] | 0 ug/L / 12.5-100 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 28 | hours | 176.5 | μg/L [Active ingredient] | 0 ug/L / 100 ug/L / 165 ug/L / 230 ug/L / 295 ug/L / 360 ug/L / 425 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 24 | hours | 179.87 | μg/L [Active ingredient] | 0 ug/L / 12.5-100 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 1 | hours | 1.26 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fochtman,P., A. Raszka, and E. Nierzedska | The Use of Conventional Bioassays, Microbiotests, and Some "Rapid" Methods in the Selection of an Optimal Test Battery for the Assessment of Pesticides Toxicity | Environ. Toxicol.15(5) | 2000 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 25 | hours | 79.53 | μg/L [Active ingredient] | 0 ug/L / 12.5-100 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 25-200 ug/L / 0 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >50～<100 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >150～<200 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 73.1 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 68.7 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >100～<150 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | >50～<100 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 25-200 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 156.66 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 145.3 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 103 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC10 EC10 | 48 | hours | 162 | μg/L [Formulation] | 0 ug/L / 2.2-2550 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC10 EC10 | 48 | hours | 58 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | LC50 LC50 | 48 | hours | 460 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H. | The Toxicity of Benomyl, Thiophanate-Methyl, and BCM to Four Freshwater Organisms | Bull. Environ. Contam. Toxicol.16(2) | 1976 | |||||||
| 甲殻類 | Daphnia magna | Feeding behaviorFood consumption | EC50 EC50 | 27 | hours | 196.21 | μg/L [Active ingredient] | 0 ug/L / 12.5-100 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | MortalityMortality | EC50 EC50 | 24 | hours | 22.9 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | ReproductionReproduction, general | EC50 EC50 | 48 | hours | 20 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H. | The Toxicity of Benomyl, Thiophanate-Methyl, and BCM to Four Freshwater Organisms | Bull. Environ. Contam. Toxicol.16(2) | 1976 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | EC50 EC50 | 24 | hours | 136.9 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ferreira,A.L.G., S. Loureiro, and A.M.V.M. Soares | Toxicity Prediction of Binary Combinations of Cadmium, Carbendazim and Low Dissolved Oxygen on Daphnia magna | Aquat. Toxicol.89 | 2008 | |||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 48 | hours | 350 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | LOEC | 21 | days | 25 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 甲殻類 | Chironomus yoshimatsui | 羽化率 | LOEC | 28 | days | 12.1 | mg/kg | ○ | 80, 40, 20, 10, 5.0mg/kg, 対照区 | 48.6, 23.5, 12.1, 6.04, 3.07mg/kg（暴露開始時） | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
| 甲殻類 | Daphnia magna | NOEL | 21 | days | 3.1 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 甲殻類 | Daphnia magna | NOEL | 21 | days | 13 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 甲殻類 | Americamysis bahia | LOEC | 28 | days | 50.4 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 甲殻類 | Americamysis bahia | NOEL | 28 | days | 24.8 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 甲殻類 | Daphnia magna | LOEC | 21 | days | 6.6 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 甲殻類 | Daphnia magna | Reproduction | EC10 | 18 | days | 16 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | B | Canton, J.H. | The Toxicity of Benomyl, Thiophanate-Methyl, and BCM to Four Freshwater Organisms. | Bull.Environ.Contam.Toxicol. 16(2) | 1976 | 2020/02/21 | |||||
| 甲殻類 | Chironomus yoshimatsui | 変態速度 | NOEC | 28 | days | 3.07 | mg/kg | ○ | 80, 40, 20, 10, 5.0mg/kg, 対照区 | 48.6, 23.5, 12.1, 6.04, 3.07mg/kg（暴露開始時） | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
| 甲殻類 | Chironomus yoshimatsui | 変態速度 | EC50 | 28 | days | 13.6 | mg/kg | ○ | 80, 40, 20, 10, 5.0mg/kg, 対照区 | 48.6, 23.5, 12.1, 6.04, 3.07mg/kg（暴露開始時） | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
| 甲殻類 | Chironomus yoshimatsui | 羽化率 | EC50 | 28 | days | 9.99 | mg/kg | ○ | 80, 40, 20, 10, 5.0mg/kg, 対照区 | 48.6, 23.5, 12.1, 6.04, 3.07mg/kg（暴露開始時） | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
| 甲殻類 | Reproduction | NOEC | 21 | days | 0.0015 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | EFSA | Conclusion on the peer review of the pesticide risk assessment of the active substance carbendazim | http://dx.doi.org/10.2903/j.efsa.2010.1598 | 2010 | 2020/03/26 | |||||||
| 甲殻類 | Daphnia magna | Reproduction | NOEC | 15 | days | 37.5 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | C | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim. | Aquat. Toxicol.102(1/2) | 2011 | 2020/02/18 | |||||
| 甲殻類 | Chironomus yoshimatsui | 羽化率 | NOEC | 28 | days | 6.04 | mg/kg | ○ | 80, 40, 20, 10, 5.0mg/kg, 対照区 | 48.6, 23.5, 12.1, 6.04, 3.07mg/kg（暴露開始時） | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
| 甲殻類 | Chironomus yoshimatsui | 変態速度 | LOEC | 28 | days | 6.04 | mg/kg | ○ | 80, 40, 20, 10, 5.0mg/kg, 対照区 | 48.6, 23.5, 12.1, 6.04, 3.07mg/kg（暴露開始時） | 1 日本環境省 生態リスク初期評価 | 2020/01/28 | |||||||
| 甲殻類 | Daphnia magna | PopulationIntrinsic rate of increase | EC50 EC50 | 21 | days | 40 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | ReproductionFecundity | EC50 EC50 | 21 | days | 40.05 | μg/L [Active ingredient] | 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | ReproductionAbort | EC50 EC50 | 21 | days | 49.19 | μg/L [Active ingredient] | 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | ReproductionProgeny counts/numbers | EC50 EC50 | 21 | days | >30～<40 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 21 | days | 53 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | PopulationIntrinsic rate of increase | EC50 EC50 | 21 | days | >30～<40 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | ReproductionFecundity | EC50 EC50 | 21 | days | 206.2 | μg/L [Active ingredient] | 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L / 65 ug/L / 80 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | ReproductionReproduction, general | EC50 EC50 | 21 | days | 46.62 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 14 | days | >150 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | ReproductionFecundity | EC50 EC50 | 21 | days | 47.19 | μg/L [Active ingredient] | 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | ReproductionProgeny counts/numbers | EC50 EC50 | 21 | days | >30～<40 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | ReproductionProgeny counts/numbers | EC50 EC50 | 21 | days | >20～<30 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | ReproductionFecundity | LOEC LOEC | 21 | days | 20 | μg/L [Active ingredient] | 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L / 65 ug/L / 80 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | ReproductionReproduction, general | LOEC LOEC | 21 | days | 50 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC10 EC10 | 25 | days | 30 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | ReproductionAbort | EC50 EC50 | 21 | days | 28.8 | μg/L [Active ingredient] | 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L / 65 ug/L / 80 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | ReproductionHatch | LOEC LOEC | 21 | days | 6.6 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | MortalitySurvival | LOEC LOEC | 21 | days | 50 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | ReproductionHatch | LOEC LOEC | 21 | days | 0.025 | ppm [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 14 | days | 55 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | ReproductionAbort | EC50 EC50 | 21 | days | 42.73 | μg/L [Active ingredient] | 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | ReproductionAbort | EC50 EC50 | 21 | days | 50.2 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 14 | days | 63 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 21 | days | 49 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | ReproductionFecundity | EC50 EC50 | 21 | days | 44.63 | μg/L [Active ingredient] | 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 21 | days | 79 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 14 | days | 76 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 21 | days | 50 | μg/L [Active ingredient] | 0 ug/L / 62 (49-71) ug/L / 111 (97-128) ug/L / 170 (147-194) ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Del Arco,A.I., A. Rico, and P.J. Van den Brink | Effects of Intra- and Interspecific Competition on the Sensitivity of Daphnia magna Populations to the Fungicide Carbendazim | Ecotoxicology24(6) | 2015 | ||||||
| 甲殻類 | Daphnia magna | ReproductionAbort | LOEC LOEC | 21 | days | 35 | μg/L [Active ingredient] | 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L / 65 ug/L / 80 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | ReproductionFecundity | EC50 EC50 | 21 | days | 44.77 | μg/L [Active ingredient] | 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | ReproductionAbort | NOEC NOEC | 21 | days | 20 | μg/L [Active ingredient] | 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L / 65 ug/L / 80 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | ReproductionReproduction, general | MATC | 21 | days | 0.045 | mg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Fochtman,P., A. Raszka, and E. Nierzedska | The Use of Conventional Bioassays, Microbiotests, and Some "Rapid" Methods in the Selection of an Optimal Test Battery for the Assessment of Pesticides Toxicity | Environ. Toxicol.15(5) | 2000 | |||||||
| 甲殻類 | Daphnia magna | ReproductionReproduction, general | NOEC NOEC | 21 | days | 37.5 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | ReproductionHatch | NOEC NOEC | 21 | days | 0.013 | ppm [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | ReproductionHatch | NOEC NOEC | 21 | days | 3.1 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | ReproductionFecundity | LOEC LOEC | 25 | days | 92.8 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | NOEC NOEC | 14 | days | 3.3 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van den Brink,P.J., J. Hattink, F. Bransen, E. Van Donk, and T.C.M. Brock | Impact of the Fungicide Carbendazim in Freshwater Microcosms. II. Zooplankton, Primary Producers and Final Conclusions | Aquat. Toxicol.48(2-3) | 2000 | |||||||
| 甲殻類 | Daphnia magna | ReproductionFecundity | NOEC NOEC | 25 | days | 25.8 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | PopulationIntrinsic rate of increase | EC50 EC50 | 21 | days | >40～<50 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | ReproductionAbort | EC50 EC50 | 21 | days | 54 | μg/L [Active ingredient] | 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | ReproductionAbort | EC50 EC50 | 21 | days | 44.44 | μg/L [Active ingredient] | 0 ug/L / 12.5-75 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Ribeiro,F., N.C.G. Ferreira, A. Ferreira, A.M.V.M. Soares, and S. Loureiro | Is Ultraviolet Radiation a Synergistic Stressor in Combined Exposures? The Case Study of Daphnia magna Exposure to UV and Carbendazim | Aquat. Toxicol.102(1/2) | 2011 | ||||||
| 甲殻類 | Daphnia magna | MortalitySurvival | LOEC LOEC | 21 | days | 0.1 | ppm [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 甲殻類 | Daphnia magna | ReproductionFecundity | NOEC NOEC | 21 | days | 5 | μg/L [Active ingredient] | 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L / 65 ug/L / 80 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | IntoxicationImmobile | EC50 EC50 | 25 | days | 44 | μg/L [Formulation] | 0 ug/L / 2.2-297 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van Wijngaarden,R.P.A., S.J.H. Crum, K. Decraene, J. Hattink, and A. Van Kammen | Toxicity of Derosal (Active Ingredient Carbendazim) to Aquatic Invertebrates | Chemosphere37(4) | 1998 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | LOEC LOEC | 14 | days | 33 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van den Brink,P.J., J. Hattink, F. Bransen, E. Van Donk, and T.C.M. Brock | Impact of the Fungicide Carbendazim in Freshwater Microcosms. II. Zooplankton, Primary Producers and Final Conclusions | Aquat. Toxicol.48(2-3) | 2000 | |||||||
| 甲殻類 | Daphnia magna | ReproductionProgeny counts/numbers | EC50 EC50 | 21 | days | >20～<30 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | PopulationIntrinsic rate of increase | EC50 EC50 | 21 | days | 30 | μg/L [Active ingredient] | 0 ug/L / 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J.L.T. Pestana, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Multigenerational Effects of Carbendazim in Daphnia magna | Environ. Toxicol. Chem.36(2) | 2017 | ||||||
| 甲殻類 | Daphnia magna | PopulationAbundance | EC50 EC50 | 28 | days | 37 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Van den Brink,P.J., J. Hattink, F. Bransen, E. Van Donk, and T.C.M. Brock | Impact of the Fungicide Carbendazim in Freshwater Microcosms. II. Zooplankton, Primary Producers and Final Conclusions | Aquat. Toxicol.48(2-3) | 2000 | |||||||
| 甲殻類 | Daphnia magna | MortalityMortality | NR-LETH | 21 | days | 65 | μg/L [Active ingredient] | 0 ug/L / 5 ug/L / 20 ug/L / 35 ug/L / 50 ug/L / 65 ug/L / 80 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Silva,A.R.R., D.N. Cardoso, A. Cruz, J. Lourenco, S. Mendo, A.M.V.M. Soares, and S. Loureiro | Ecotoxicity and Genotoxicity of a Binary Combination of Triclosan and Carbendazim to Daphnia magna | Ecotoxicol. Environ. Saf.115 | 2015 | ||||||
| 甲殻類 | Daphnia magna | NOEL | 21 | days | 13 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Buikema | 1989 | 2018/02/28 | |||||||||
| 甲殻類 | Daphnia magna | LOEC | 21 | days | 25 | ppb | 3 USEPA Pesticide Ecotoxicity Database | A. Buikema | 1989 | 2018/02/28 | |||||||||
| 魚類 | Danio rerio (Zebrafish) | BehaviorDistance moved, change in direct movement | LOEC LOEC | 96 | hours | 4 | μg/L [Active ingredient] | 0 ug/L / 0.16 ug/L / 0.8 ug/L / 4 ug/L / 20 ug/L / 100 ug/L / 500 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | BehaviorDistance moved, change in direct movement | LOEC LOEC | 96 | hours | 500 | μg/L [Active ingredient] | 0 ug/L / 0.16 ug/L / 0.8 ug/L / 4 ug/L / 20 ug/L / 100 ug/L / 500 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | BehaviorSwimming | LOEC LOEC | 96 | hours | 0.16 | μg/L [Active ingredient] | 0 ug/L / 0.16 ug/L / 0.8 ug/L / 4 ug/L / 20 ug/L / 100 ug/L / 500 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | BehaviorDistance moved, change in direct movement | NOEC NOEC | 96 | hours | 100 | μg/L [Active ingredient] | 0 ug/L / 0.16 ug/L / 0.8 ug/L / 4 ug/L / 20 ug/L / 100 ug/L / 500 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | BehaviorDistance moved, change in direct movement | NOEC NOEC | 96 | hours | 0.8 | μg/L [Active ingredient] | 0 ug/L / 0.16 ug/L / 0.8 ug/L / 4 ug/L / 20 ug/L / 100 ug/L / 500 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | BehaviorDistance moved, change in direct movement | NOEC NOEC | 96 | hours | 100 | μg/L [Active ingredient] | 0 ug/L / 0.16 ug/L / 0.8 ug/L / 4 ug/L / 20 ug/L / 100 ug/L / 500 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | BehaviorDistance moved, change in direct movement | NOEC NOEC | 96 | hours | 500 | μg/L [Active ingredient] | 0 ug/L / 0.16 ug/L / 0.8 ug/L / 4 ug/L / 20 ug/L / 100 ug/L / 500 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | BehaviorDistance moved, change in direct movement | LOEC LOEC | 96 | hours | 500 | μg/L [Active ingredient] | 0 ug/L / 0.16 ug/L / 0.8 ug/L / 4 ug/L / 20 ug/L / 100 ug/L / 500 ug/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Lepomis macrochirus (Bluegill) | NOEL | 96 | hours | 1850 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/12/04 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 145 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/11/29 | ||||||||||
| 魚類 | Pimephales promelas (Fathead minnow) | LC50 | 96 | hours | >10000 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/11/29 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 320 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/11/29 | ||||||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | LC50 | 96 | hours | >1.158 | mg/L | 10 EHC (Environmental Health Criteria) | Boeri RL | Static acute toxicity of carbendazim technical to the sheepshead minnow, Cyprinodon variegatus. | Marblehead, Massachusetts, Enseco (Unpublished report No. HLO 12-89, prepared for E.I. Du Pont de Nemours and Co., Inc.). | 1988 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 370 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/11/29 | ||||||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | >3.2 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | 5.5 | mg/L | 10 EHC (Environmental Health Criteria) | Wetzel JW & Hutton DG | 96-Hour LC50 to bluegill sunfish. | Newark, Delaware, E.I. Du Pont de Nemours and Co., Inc., Haskell Laboratory (Unpublished report No. HLR 401-84) | 1984 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.88 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | LC50 | 96 | hours | >1850 | ppb | 3 USEPA Pesticide Ecotoxicity Database | C | 2019/11/29 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.145 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.78 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.34 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.41 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.37 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.32 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.87 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.64 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.1 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.87 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | >1.8 | mg/L | 10 EHC (Environmental Health Criteria) | Palawski DU & Knowles CO | Toxicological studies of benomyl and carbendazim in rainbow trout, channel catfish and bluegills. | Environ Toxicol Chem, 5 | 1986 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.36 | mg/L | 10 EHC (Environmental Health Criteria) | Heinemann JM | Acute static fish (rainbow trout) toxicity study - freshwater (MBC). | Vienna, Virginia, Hazelton Laboratories (Unpublished report No. HLO-150-71, prepared for E.I. Du Pont de Nemours and Co., Inc.) | 1971 | 2019/12/18 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 48 | hours | 1.8 | mg/L | 10 EHC (Environmental Health Criteria) | Canton JH | The toxicity of benomyl, thiophanate-methyl, and BLM to four freshwater organisms. | Bull Environ Contam Toxicol, 16 | 1976 | 2019/12/18 | |||||||
| 魚類 | Mortality | LC50 | 48 | hours | 0.0209 | 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 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 2 | days | 1800 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | C | Canton, J.H. | The Toxicity of Benomyl, Thiophanate-Methyl, and BCM to Four Freshwater Organisms. | Bull.Environ.Contam.Toxicol. 16(2) | 1976 | 2020/02/18 | |||||
| 魚類 | Lepomis macrochirus (Bluegill) | Mortality | LC50 | 4 | days | >3200 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | B | Palawski, D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills. | Environ.Toxicol.Chem. 5(12) | 1986 | 2020/02/18 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | Mortality | LC50 | 4 | days | 100 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | B | Palawski, D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills. | Environ.Toxicol.Chem. 5(12) | 1986 | 2020/03/26 | |||||
| 魚類 | Poecilia reticulata (Guppy) | Mortality | LC50 | 2 | days | >8000 | μg/L | 6 日本環境省 化学物質の環境リスク評価（生態リスク初期評価） | C | Canton, J.H. | The Toxicity of Benomyl, Thiophanate-Methyl, and BCM to Four Freshwater Organisms. | Bull.Environ.Contam.Toxicol. 16(2) | 1976 | 2020/02/18 | |||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 0.41 | mg/L | 18 既存化学物質安全性(ハザード)評価シート | EHC | 1993 | 2020/01/08 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | 130 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/12/04 | ||||||||||
| 魚類 | Growth | NOEC | 21 | days | 0.0032 | mg/L | 17 Aquatic OASIS (OECD QSAR Toolbox) | EFSA | Conclusion on the peer review of the pesticide risk assessment of the active substance carbendazim | http://dx.doi.org/10.2903/j.efsa.2010.1598 | 2010 | ||||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | LC50 | 96 | hours | >1158 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/11/29 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 1320 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/11/29 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 230 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/11/29 | ||||||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | NOEL | 96 | hours | 1158 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/12/04 | ||||||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | NOEL | 96 | hours | 1158 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/12/04 | ||||||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | LC50 | 96 | hours | >1158 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/12/04 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 96 | hours | <180 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/12/04 | ||||||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC10 EC10 | 96 | hours | 1.41 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC10 EC10 | 72 | hours | 1.39 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentDeformation | EC10 EC10 | 24 | hours | 1.27 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityHatch | EC10 EC10 | 96 | hours | 1.54 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC10 EC10 | 96 | hours | 1.31 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityHatch | EC50 EC50 | 96 | hours | 1.62 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC50 EC50 | 96 | hours | 1.53 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC50 EC50 | 72 | hours | 1.46 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentDeformation | EC50 EC50 | 24 | hours | 1.48 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC50 EC50 | 96 | hours | 1.46 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyLength | EC50 EC50 | 96 | hours | 1.35 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityHatch | EC50 EC50 | 72 | hours | 1.57 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC50 EC50 | 96 | hours | 1.54 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentSlowed, Retarded, Delayed or Non-development | EC50 EC50 | 48 | hours | 1.59 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | GrowthLength | EC50 EC50 | 96 | hours | 1.72 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC50 EC50 | 48 | hours | 1.6 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyLength | EC10 EC10 | 96 | hours | 1.33 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentStage | EC50 EC50 | 48 | hours | 1.86 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC10 EC10 | 96 | hours | 1.38 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC50 EC50 | 72 | hours | 1.52 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC50 EC50 | 72 | hours | 1.52 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC10 EC10 | 48 | hours | 1.55 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC10 EC10 | 72 | hours | 1.33 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentStage | EC10 EC10 | 48 | hours | 1.18 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC10 EC10 | 72 | hours | 1.44 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | DevelopmentSlowed, Retarded, Delayed or Non-development | EC10 EC10 | 48 | hours | 1.56 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | GrowthLength | EC10 EC10 | 96 | hours | 1.42 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC50 LC50 | 72 | hours | 1.74 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityHatch | EC10 EC10 | 72 | hours | 1.5 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC50 EC50 | 48 | hours | 1.53 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Cyprinus carpio (Carp) | MortalityMortality | LC100 LC100/ | 24 | hours | <1000 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gillet,C., and P. Roubaud | Prehatching Survival of Carp Eggs After Treatment During Fertilization and Early Development with the Antimitotic Fungicide Carbendazim | Water Res.17(10) | 1983 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 145 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 780 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 340 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 24 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 320 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 880 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 870 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 230 | ppb [Not coded] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 370 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 870 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | >1800 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 410 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Cyprinus carpio (Carp) | MortalityMortality | LC100 LC100/ | 0.5 | hours | <5000 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gillet,C., and P. Roubaud | Prehatching Survival of Carp Eggs After Treatment During Fertilization and Early Development with the Antimitotic Fungicide Carbendazim | Water Res.17(10) | 1983 | |||||||
| 魚類 | Cyprinus carpio (Carp) | MortalityMortality | LC100 LC100/ | 0.5 | hours | <5000 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gillet,C., and P. Roubaud | Prehatching Survival of Carp Eggs After Treatment During Fertilization and Early Development with the Antimitotic Fungicide Carbendazim | Water Res.17(10) | 1983 | |||||||
| 魚類 | Cyprinus carpio (Carp) | MortalityMortality | LC100 LC100/ | 0.5 | hours | <2500 | μg/L [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Gillet,C., and P. Roubaud | Prehatching Survival of Carp Eggs After Treatment During Fertilization and Early Development with the Antimitotic Fungicide Carbendazim | Water Res.17(10) | 1983 | |||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | MortalityMortality | NOEL NOEL | 96 | hours | 1160 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | MortalityMortality | NOEL NOEL | 96 | hours | 1850 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | MortalityMortality | LC50 LC50 | 96 | hours | >1160 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | MortalityMortality | LC50 LC50 | 96 | hours | >3200 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Lepomis macrochirus (Bluegill) | MortalityMortality | LC50 LC50 | 96 | hours | >1850 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC50 LC50 | 96 | hours | 1.25 | μM [Formulation] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Schmidt,S., W. Busch, R. Altenburger, and E. Kuster | Mixture Toxicity of Water Contaminants-Effect Analysis Using the Zebrafish Embryo Assay (Danio rerio) | Chemosphere152 | 2016 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 48 | hours | 1800 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Canton,J.H. | The Toxicity of Benomyl, Thiophanate-Methyl, and BCM to Four Freshwater Organisms | Bull. Environ. Contam. Toxicol.16(2) | 1976 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC10 LC10 | 48 | hours | 1.7 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 640 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 100 | μg/L [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Palawski,D.U., and C.O. Knowles | Toxicological Studies of Benomyl and Carbendazim in Rainbow Trout, Channel Catfish and Bluegills | Environ. Toxicol. Chem.5(12) | 1986 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC10 LC10 | 72 | hours | 1.63 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC10 LC10 | 96 | hours | 1.48 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC50 LC50 | 48 | hours | 1.75 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | NOEL NOEL | 96 | hours | <180 | ppb [Not coded] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | NOEL NOEL | 96 | hours | 130 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MortalityMortality | LC10 LC10 | 96 | hours | 1.76 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | MortalityMortality | LC50 LC50 | 96 | hours | 1320 | ppb [Active ingredient] | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | U.S. Environmental Protection Agency | Pesticide Ecotoxicity Database (Formerly: Environmental Effects Database (EEDB)) | Environmental Fate and Effects Division, U.S.EPA, Washington, D.C. | 1992 | |||||||
| 魚類 | Danio rerio (Zebrafish) | MorphologyAbnormal | EC10 EC10 | 48 | hours | 1.42 | mg/L [Active ingredient] | 0 mg/L / 1.09-1.24 mg/L / 1.22-1.47 mg/L / 1.26-1.55 mg/L / 1.41-1.55 mg/L / 1.50-1.70 mg/L / 1.75-1.80 mg/L / 1.84-1.94 mg/L | 16 US EPA AQUIRE (AQUatic toxicity Information REtrieval) | Andrade,T.S., J.F. Henriques, A.R. Almeida, A.L. Machado, O. Koba, P.T. Giang, A.M.V.M. Soares, and I. Domingues | Carbendazim Exposure Induces Developmental, Biochemical and Behavioural Disturbance in Zebrafish Embryos | Aquat. Toxicol.170 | 2016 | ||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LC50 | 96 | hours | 650 | ppb | 3 USEPA Pesticide Ecotoxicity Database | Core | secondary source | 1982 | 2019/11/29 | ||||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | LC50 | 96 | hours | >1158 | ppb | 3 USEPA Pesticide Ecotoxicity Database | W. Erickson | 1989 | 2018/02/28 | |||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | LOEC | 79 | days | 34 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/12/04 | ||||||||||
| 魚類 | Oncorhynchus mykiss (Rainbow trout) | NOEL | 79 | days | 11 | ppb | 3 USEPA Pesticide Ecotoxicity Database | S | 2019/12/04 | ||||||||||
| 魚類 | Cyprinodon variegatus (Sheepshead minnow) | NOEL | 96 | hours | 1158 | ppb | 3 USEPA Pesticide Ecotoxicity Database | W. Erickson | 1989 | 2018/02/28 |