Bradberry Sally M, Cage Sarah A, Proudfoot Alex T, Vale J Allister
National Poisons Information Service (Birmingham Centre), City Hospital, UK.
Toxicol Rev. 2005;24(2):93-106. doi: 10.2165/00139709-200524020-00003.
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.
第一种拟除虫菊酯类杀虫剂丙烯菊酯于1949年被发现。丙烯菊酯和其他具有基本环丙烷羧酸酯结构的拟除虫菊酯为I型拟除虫菊酯。通过添加氰基进一步增强了这些合成拟除虫菊酯的杀虫活性,从而得到α-氰基(II型)拟除虫菊酯,如氯氰菊酯。在一组缺乏环丙烷环但含有α-氰基(因此为II型拟除虫菊酯)的苯乙酸3-苯氧基苄酯中发现了杀虫活性,这促使了氰戊菊酯及相关化合物的开发。所有拟除虫菊酯至少可以以四种立体异构体的形式存在,每种异构体具有不同的生物活性。它们作为外消旋混合物或单一异构体销售。在商业配方中, 通常通过添加增效剂如胡椒基丁醚来增强拟除虫菊酯的活性,胡椒基丁醚可抑制活性成分的代谢降解。拟除虫菊酯在家庭和商业上被广泛用作杀虫剂,在医学上用于局部治疗疥疮和头虱。在热带国家,作为抗疟疾策略的一部分,蚊帐通常浸泡在溴氰菊酯溶液中。拟除虫菊酯对昆虫的毒性比对哺乳动物高约2250倍,因为昆虫的钠通道敏感性增加、体型较小且体温较低。此外,哺乳动物因皮肤吸收不良和快速代谢为无毒代谢物而受到保护。拟除虫菊酯单独产生毒性的机制很复杂,当它们与胡椒基丁醚或有机磷杀虫剂或两者共同配制时会变得更加复杂,因为这些化合物会抑制拟除虫菊酯的代谢。拟除虫菊酯的主要作用于钠通道和氯通道。拟除虫菊酯改变电压敏感钠通道的门控特性以延迟其关闭。随后会出现持久的钠内流(称为钠“尾电流”),如果其足够大或足够长,会降低动作电位阈值并导致重复放电;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阻止进一步的动作电位产生,继而出现“传导阻滞”。只需低浓度的拟除虫菊酯就能改变感觉神经元功能。II型拟除虫菊酯还会通过电压依赖性氯通道降低氯电流,这种作用可能是II型拟除虫菊酯中毒特征的主要原因。在相对较高的浓度下,拟除虫菊酯还可作用于γ-氨基丁酸(GABA)门控氯通道,这可能是严重II型中毒时出现惊厥的原因。尽管它们在全球广泛使用,但关于人类拟除虫菊酯中毒的报告相对较少。据报道,因摄入或职业接触导致的死亡少于10例。在职业方面,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,但在密闭空间使用拟除虫菊酯时会增加。皮肤接触的主要不良反应是感觉异常,可能是由于皮肤感觉神经纤维的活动过度。面部最常受到影响,热、阳光、抓挠、出汗或用水等感觉刺激会加剧感觉异常。摄入拟除虫菊酯后几分钟内会出现喉咙痛、恶心、呕吐和腹痛。可能会出现口腔溃疡、分泌物增多和/或吞咽困难。全身效应在接触后4 - 48小时出现。头晕、头痛和疲劳很常见,心悸、胸闷和视力模糊较少见。昏迷和抽搐是主要的危及生命的特征。大多数患者在6天内康复,尽管在一个系列的573例病例中有7例死亡,在另一个系列的48例病例中有1例死亡。治疗以支持治疗为主。由于感觉异常通常在12 - 24小时内消退,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)可能会减轻其严重程度。