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氟虫腈光降解途径的阐明。

Elucidation of fipronil photodegradation pathways.

作者信息

Ngim K K, Mabury S A, Crosby D G

机构信息

Department of Environmental Toxicology, University of California, One Shields Avenue, Davis, California 95616, USA.

出版信息

J Agric Food Chem. 2000 Oct;48(10):4661-5. doi: 10.1021/jf9913007.

Abstract

The phenylpyrazole insecticide fipronil (I) photolyzes to its desthio product (II) in aqueous solution. However, the necessity of an intervening oxidation to a sulfone intermediate (III) has not been resolved, and the photodegradation products of II have not been identified. Using GC-MS, HPLC-UV/vis, electrospray MS, (19)F NMR, and GC-TSD, our objective was to characterize the photodegradation pathways of I, which would clarify the role of III, identify products of II, and explain unbalanced mass accounts in previous studies. Findings showed that II is formed directly and photochemically from I, confirmed by the greater stability of III (t(1/2) 112 h), and that successive oxidations of I to III and then a sulfonate (IV) comprise a second pathway. Compound II underwent photodechlorination, substitution of chlorine by trifluoromethyl, and pyrazole ring cleavage. This work is significant to understanding the photochemistry of novel phenylpyrazole pesticides in the environment.

摘要

苯基吡唑类杀虫剂氟虫腈(I)在水溶液中光解生成其脱硫产物(II)。然而,是否需要经过氧化生成砜中间体(III)这一问题尚未解决,且II的光降解产物也未得到鉴定。我们利用气相色谱 - 质谱联用仪(GC-MS)、高效液相色谱 - 紫外/可见光谱仪(HPLC-UV/vis)、电喷雾质谱仪(electrospray MS)、氟核磁共振仪((19)F NMR)以及气相色谱 - 热离子检测器(GC-TSD),旨在表征I的光降解途径,这将阐明III的作用,鉴定II的产物,并解释先前研究中质量平衡不平衡的问题。研究结果表明,II是由I直接光化学形成的,这一点通过III更高的稳定性(半衰期t(1/2)为112小时)得到证实,且I依次氧化为III,然后再氧化为磺酸盐(IV)构成了第二条途径。化合物II发生了光脱氯反应、氯被三氟甲基取代以及吡唑环裂解。这项工作对于理解新型苯基吡唑类农药在环境中的光化学性质具有重要意义。

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