拟除虫菊酯引起的中毒。

Sally M Bradberry, Sarah A Cage, Alex T Proudfoot, J Allister Vale
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引用次数: 524

摘要

1949年发现了第一种拟除虫菊酯杀虫剂——丙烯菊酯。丙烯菊酯和其他具有环丙烷羧酸酯基本结构的拟除虫菊酯为I型拟除虫菊酯。这些合成的拟除虫菊酯的杀虫活性通过添加氰基进一步增强,得到-氰基(II型)拟除虫菊酯,如氯氰菊酯。一组苯基乙酸3-苯氧苄酯(phenylacetic 3-phenoxybenzyl酯)缺乏环丙烷环,但含有-氰基(因此是II型拟除虫菊酯),其杀虫活性的发现导致了氰戊酸酯和相关化合物的发展。所有拟除虫菊酯都能以至少四种立体异构体存在,每一种都具有不同的生物活性。它们以外消旋混合物或单异构体的形式销售。在商业配方中,拟除虫菊酯的活性通常通过添加增效剂(如胡椒酰丁醇)来增强,这种增效剂可以抑制活性成分的代谢降解。拟除虫菊酯类杀虫剂广泛用于家庭和商业用途,以及用于局部治疗疥疮和头虱的药物。在热带国家,作为抗疟疾战略的一部分,蚊帐通常浸泡在溴氰菊酯溶液中。拟除虫菊酯类杀虫剂对昆虫的毒性是哺乳动物的2250倍,因为昆虫对钠通道的敏感度更高,体型更小,体温更低。此外,哺乳动物的皮肤吸收能力差,对无毒代谢物的代谢速度快,这也保护了哺乳动物。拟除虫菊酯单独产生毒性的机制是复杂的,当它们与胡椒酰丁醇或有机磷杀虫剂或两者共同配制时变得更加复杂,因为这些化合物抑制拟除虫菊酯的代谢。拟除虫菊酯主要作用于钠通道和氯通道。拟除虫菊酯可以改变电压敏感钠通道的门控特性,延缓其关闭。持续的钠流入(称为钠“尾电流”)随之而来,如果它足够大和/或长,降低动作电位阈值并引起重复放电;这可能是引起感觉异常的机制。在高拟除虫菊酯浓度下,钠尾电流可能足够大,以防止进一步的动作电位产生和“传导阻滞”。只有低拟除虫菊酯浓度才能改变感觉神经元的功能。II型拟除虫菊酯还能通过电压依赖性氯离子通道降低氯离子电流,这一作用可能是II型拟除虫菊酯中毒的最主要原因。在相对高浓度的情况下,拟除虫菊酯也可以作用于氨基丁酸门控的氯离子通道,这可能是导致严重II型中毒发作的原因。尽管它们在世界范围内广泛使用,但人类拟除虫菊酯中毒的报告相对较少。据报道,因误食或职业性接触而死亡的不到10人。职业上,拟除虫菊酯的主要吸收途径是通过皮肤。吸入的重要性要小得多,但当在密闭空间使用拟除虫菊酯时则会增加。皮肤接触的主要不良影响是感觉异常,可能是由于皮肤感觉神经纤维的过度活跃。受影响最常见的是面部,感觉刺激如热、阳光、抓挠、出汗或用水会加重感觉异常。摄入拟除虫菊酯会在几分钟内引起喉咙痛、恶心、呕吐和腹痛。可能出现口腔溃疡、分泌物增多和/或吞咽困难。全身效应发生在接触后4-48小时。头晕、头痛和疲劳是常见的,心悸、胸闷和视力模糊较少。昏迷和抽搐是危及生命的主要特征。大多数患者在6天内康复,尽管一个系列的573例中有7例死亡,另一个系列的48例中有1例死亡。管理层是支持的。由于感觉异常通常在12-24小时内消退,因此一般不需要特殊治疗,尽管局部应用dl- α生育酚醋酸酯(维生素E)可减轻其严重程度。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Poisoning due to pyrethroids.

The first pyrethroid pesticide, allethrin, was identified in 1949. Allethrin and other pyrethroids with a basic cyclopropane carboxylic ester structure are type I pyrethroids. The insecticidal activity of these synthetic pyrethroids was enhanced further by the addition of a cyano group to give alpha-cyano (type II) pyrethroids, such as cypermethrin. The finding of insecticidal activity in a group of phenylacetic 3-phenoxybenzyl esters, which lacked the cyclopropane ring but contained the alpha-cyano group (and hence were type II pyrethroids) led to the development of fenvalerate and related compounds. All pyrethroids can exist as at least four stereoisomers, each with different biological activities. They are marketed as racemic mixtures or as single isomers. In commercial formulations, the activity of pyrethroids is usually enhanced by the addition of a synergist such as piperonyl butoxide, which inhibits metabolic degradation of the active ingredient. Pyrethroids are used widely as insecticides both in the home and commercially, and in medicine for the topical treatment of scabies and headlice. In tropical countries mosquito nets are commonly soaked in solutions of deltamethrin as part of antimalarial strategies. Pyrethroids are some 2250 times more toxic to insects than mammals because insects have increased sodium channel sensitivity, smaller body size and lower body temperature. In addition, mammals are protected by poor dermal absorption and rapid metabolism to non-toxic metabolites. The mechanisms by which pyrethroids alone are toxic are complex and become more complicated when they are co-formulated with either piperonyl butoxide or an organophosphorus insecticide, or both, as these compounds inhibit pyrethroid metabolism. The main effects of pyrethroids are on sodium and chloride channels. Pyrethroids modify the gating characteristics of voltage-sensitive sodium channels to delay their closure. A protracted sodium influx (referred to as a sodium 'tail current') ensues which, if it is sufficiently large and/or long, lowers the action potential threshold and causes repetitive firing; this may be the mechanism causing paraesthesiae. At high pyrethroid concentrations, the sodium tail current may be sufficiently great to prevent further action potential generation and 'conduction block' ensues. Only low pyrethroid concentrations are necessary to modify sensory neurone function. Type II pyrethroids also decrease chloride currents through voltage-dependent chloride channels and this action probably contributes the most to the features of poisoning with type II pyrethroids. At relatively high concentrations, pyrethroids can also act on GABA-gated chloride channels, which may be responsible for the seizures seen with severe type II poisoning. Despite their extensive world-wide use, there are relatively few reports of human pyrethroid poisoning. Less than ten deaths have been reported from ingestion or following occupational exposure. Occupationally, the main route of pyrethroid absorption is through the skin. Inhalation is much less important but increases when pyrethroids are used in confined spaces. The main adverse effect of dermal exposure is paraesthesiae, presumably due to hyperactivity of cutaneous sensory nerve fibres. The face is affected most commonly and the paraesthesiae are exacerbated by sensory stimulation such as heat, sunlight, scratching, sweating or the application of water. Pyrethroid ingestion gives rise within minutes to a sore throat, nausea, vomiting and abdominal pain. There may be mouth ulceration, increased secretions and/or dysphagia. Systemic effects occur 4-48 hours after exposure. Dizziness, headache and fatigue are common, and palpitations, chest tightness and blurred vision less frequent. Coma and convulsions are the principal life-threatening features. Most patients recover within 6 days, although there were seven fatalities among 573 cases in one series and one among 48 cases in another. Management is supportive. As paraesthesiae usually resolve in 12-24 hours, specific treatment is not generally required, although topical application of dl-alpha tocopherol acetate (vitamin E) may reduce their severity.

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