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Photoinduced oxidation of the insecticide phenothrin on soil surfaces.光诱导土壤表面杀虫剂苯醚菊酯的氧化。
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4
Enantioselectivity in environmental risk assessment of modern chiral pesticides.现代手性农药环境风险评价中的对映体选择性。
Environ Pollut. 2010 Jul;158(7):2371-83. doi: 10.1016/j.envpol.2010.03.014. Epub 2010 Apr 8.
5
Isomer- and enantioselective degradation and chiral stability of fenpropathrin and fenvalerate in soils.甲氰菊酯和氰戊菊酯在土壤中的异构体和对映体选择性降解及手性稳定性
Chemosphere. 2009 Jul;76(4):509-16. doi: 10.1016/j.chemosphere.2009.03.015. Epub 2009 Apr 7.
6
Stereo and enantioselective degradation of beta-Cypermethrin and beta-Cyfluthrin in soil.土壤中高效氯氰菊酯和高效氟氯氰菊酯的立体选择性和对映体选择性降解
Bull Environ Contam Toxicol. 2008 Apr;80(4):335-9. doi: 10.1007/s00128-008-9368-y. Epub 2008 Mar 3.
7
Enantiomeric differences in permethrin degradation pathways in soil and sediment.氯菊酯在土壤和沉积物中降解途径的对映体差异。
J Agric Food Chem. 2006 Nov 29;54(24):9145-51. doi: 10.1021/jf061426l.
8
Enantioselective degradation and chiral stability of pyrethroids in soil and sediment.拟除虫菊酯在土壤和沉积物中的对映体选择性降解及手性稳定性
J Agric Food Chem. 2006 Jul 12;54(14):5040-5. doi: 10.1021/jf060329p.
9
Behavior of pesticides in water-sediment systems.农药在水-沉积物系统中的行为。
Rev Environ Contam Toxicol. 2006;187:133-251. doi: 10.1007/0-387-32885-8_4.
10
Enantioselectivity in environmental safety of current chiral insecticides.当前手性杀虫剂环境安全性中的对映体选择性。
Proc Natl Acad Sci U S A. 2005 Jan 18;102(3):701-6. doi: 10.1073/pnas.0408847102. Epub 2005 Jan 4.

氯氰菊酯在水生环境中的行为。

Behavior of cyphenothrin in aquatic environment.

作者信息

Suzuki Yusuke, Yoshida Mayumi, Sugano Terumi, Shibata Atsushi, Kodaka Rika, Fujisawa Takuo, Katagi Toshiyuki

机构信息

Environmental Health Science Laboratory, Sumitomo Chemical Co., Ltd., 4-2-1, Takatsukasa, Takarazuka, Hyogo 665-8555, Japan.

Environmental Health Science Laboratory, Sumitomo Chemical Co., Ltd., 3-1-98 Kasugadenaka, Konohana-ku, Osaka 554-8558, Japan.

出版信息

J Pestic Sci. 2017 May 20;42(2):17-24. doi: 10.1584/jpestics.D16-085.

DOI:10.1584/jpestics.D16-085
PMID:30363326
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC6173171/
Abstract

The behavior of cyphenothrin () [()-α-cyano-3-phenoxybenzyl (1)---2,2-dimethyl-3-(2-methylprop-1-enyl)cyclopropanecarboxylate] in an aquatic environment was investigated by using the C-labeled and isomers. In parallel with the rapid partition from water phase to bottom sediment, was degraded with the first-order half-lives of 2.0 (-) and 7.3 days (-) in the water-sediment system under dark conditions. underwent extensive microbial degradation ester cleavage to form 3-phenoxybenzoic acid, finally forming bound residues and mineralizing to CO. Aqueous photolysis significantly accelerated the degradation of with a half-life of <1 day, mainly photo-induced oxidation at the 2-methylprop-1-enyl group and ester cleavage without isomerization. These results strongly suggest that is unlikely to persist in the actual aquatic environment due to its rapid photolysis and extensive microbial degradation.

摘要

使用碳-14标记的氯氰菊酯()[()-α-氰基-3-苯氧基苄基(1)---2,2-二甲基-3-(2-甲基丙烯基)环丙烷羧酸酯]的异构体研究了氯氰菊酯在水生环境中的行为。与从水相快速分配到底部沉积物同时,在黑暗条件下的水-沉积物系统中,氯氰菊酯以2.0天(-)和7.3天(-)的一级半衰期降解。氯氰菊酯经历了广泛的微生物降解,酯键断裂形成3-苯氧基苯甲酸,最终形成结合残留物并矿化生成二氧化碳。水相光解显著加速了氯氰菊酯的降解,半衰期<1天,主要是在2-甲基丙烯基处的光诱导氧化和酯键断裂,没有异构体化。这些结果强烈表明,由于其快速光解和广泛的微生物降解,氯氰菊酯不太可能在实际水生环境中持续存在。