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Peer review of the pesticide risk assessment of the active substance thiacloprid.活性物质噻虫啉农药风险评估的同行评审。
EFSA J. 2019 Mar 14;17(3):e05595. doi: 10.2903/j.efsa.2019.5595. eCollection 2019 Mar.
2
metabolism of imidacloprid and acetamiprid in rainbow trout and rat.吡虫啉和啶虫脒在虹鳟鱼和大鼠体内的代谢
Xenobiotica. 2020 Jul;50(7):805-814. doi: 10.1080/00498254.2019.1694197. Epub 2019 Nov 25.
3
Characterization and analysis of estrogenic cyclic phenone metabolites produced in vitro by rainbow trout liver slices using GC-MS, LC-MS and LC-TOF-MS.采用 GC-MS、LC-MS 和 LC-TOF-MS 技术对虹鳟鱼肝切片体外产生的雌激素环状苯乙酮代谢物进行表征和分析。
J Chromatogr B Analyt Technol Biomed Life Sci. 2019 Sep 15;1126-1127:121717. doi: 10.1016/j.jchromb.2019.121717. Epub 2019 Aug 11.
4
Metabolism of Diazinon in Rainbow Trout Liver Slices.二嗪农在虹鳟鱼肝切片中的代谢
Appl In Vitro Toxicol. 2018 Mar 1;4(1):13-23. doi: 10.1089/aivt.2017.0025.
5
Metabolism of cyclic phenones in rainbow trout assays.虹鳟鱼试验中环状苯醌的代谢
Xenobiotica. 2020 Feb;50(2):192-208. doi: 10.1080/00498254.2019.1596331. Epub 2019 Apr 15.
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Imidacloprid as reproductive toxicant and endocrine disruptor: investigations in laboratory animals.吡虫啉作为生殖毒物和内分泌干扰物:对实验动物的研究
Arh Hig Rada Toksikol. 2018 Jun 1;69(2):103-108. doi: 10.2478/aiht-2018-69-3144.
7
Toxicokinetics of the neonicotinoid insecticide imidacloprid in rainbow trout (Oncorhynchus mykiss).硝基亚甲基类杀虫剂吡虫啉在虹鳟(Oncorhynchus mykiss)中的毒代动力学。
Comp Biochem Physiol C Toxicol Pharmacol. 2018 Feb;205:34-42. doi: 10.1016/j.cbpc.2018.01.002. Epub 2018 Feb 3.
8
The environmental risks of neonicotinoid pesticides: a review of the evidence post 2013.新烟碱类杀虫剂的环境风险:2013年后的证据综述
Environ Sci Pollut Res Int. 2017 Jul;24(21):17285-17325. doi: 10.1007/s11356-017-9240-x. Epub 2017 Jun 7.
9
Neurobehavioral impairments caused by developmental imidacloprid exposure in zebrafish.斑马鱼发育过程中接触吡虫啉所致的神经行为损伤。
Neurotoxicol Teratol. 2015 May-Jun;49:81-90. doi: 10.1016/j.ntt.2015.04.006. Epub 2015 May 2.
10
Oxidative stress and DNA damage induced by imidacloprid in zebrafish (Danio rerio).吡虫啉对斑马鱼(Danio rerio)诱导的氧化应激和DNA损伤。
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采用液相色谱-紫外检测法和高分辨率质谱法对噻虫啉在虹鳟鱼和大鼠体内的代谢进行评估。

metabolism assessment of thiacloprid in rainbow trout and rat by LC-UV and high resolution-mass spectrometry.

作者信息

Serrano Jose, Kolanczyk Richard C, Blackwell Brett R, Sheedy Barbara R, Tapper Mark A

机构信息

Office of Research and Development, Center for Computational Toxicology and Exposure, Great Lakes Toxicology and Ecology Division, United States Environmental Protection Agency, Duluth, MN, USA.

出版信息

Xenobiotica. 2021 May;51(5):536-548. doi: 10.1080/00498254.2020.1840658. Epub 2021 Mar 15.

DOI:10.1080/00498254.2020.1840658
PMID:33086928
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC9536423/
Abstract

Thiacloprid (THI) is a widely used neonicotinoid insecticide where concerns have been raised regarding low absorption by crops, substantial distribution in surrounding areas, and potential adverse effects to terrestrial and aquatic organisms.Prior to this study, there was very limited information addressing the (precision-cut liver slices) metabolism of THI by fish species and the metabolic pathways regulating its potential for adverse effects.The and biotransformation pathway of THI is defined by the formation of three primary metabolites (TM1, TM2 and TM3) via separate paths differentiated by reductive decyanation, reductive dechlorination with hydration and dealkylation processes, respectively.Kinetic rates were calculated for the rat microsomal decyanation of THI into TM1 ( = 299.2 µM and = 5.3 pmol/min/mg), and for the dealkylation of THI into TM3 ( = 368.9 µM and = 3.95 pmol/min/mg).Formation confirmation and identity inference of THI metabolites in absence of standards were achieved by LC-UV and High Resolution-MS strategies.The and metabolic products of THI are conserved both across species (rat and Rainbow trout) and levels of biological organization (microsomes and liver slices), as previously reported for the neonicotinoid insecticides Imidacloprid and Acetamiprid.

摘要

噻虫啉(THI)是一种广泛使用的新烟碱类杀虫剂,人们对其在作物中的低吸收率、在周边地区的大量分布以及对陆地和水生生物的潜在不利影响表示担忧。在本研究之前,关于鱼类对THI的(精密切割肝切片)代谢以及调节其潜在不利影响的代谢途径的信息非常有限。THI的生物转化途径是通过分别经由还原脱氰、加水还原脱氯和脱烷基化过程形成三种主要代谢物(TM1、TM2和TM3)来定义的。计算了大鼠微粒体将THI脱氰生成TM1的动力学速率(Km = 299.2 μM,Vmax = 5.3 pmol/min/mg),以及将THI脱烷基生成TM3的动力学速率(Km = 368.9 μM,Vmax = 3.95 pmol/min/mg)。在没有标准品的情况下,通过LC-UV和高分辨率质谱策略实现了THI代谢物的形成确认和身份推断。正如先前对新烟碱类杀虫剂吡虫啉和啶虫脒的报道,THI的代谢产物在物种(大鼠和虹鳟鱼)和生物组织水平(微粒体和肝切片)上都是保守的。