杀虫剂对种内变异的选择性影响:在考虑污染物对环境的影响时应吸取的教训

John Baker
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引用次数: 11

摘要

杀虫剂的使用创造了有利于暴露于杀虫剂的许多物种产生抗药性的环境。接触杀虫剂也导致一些非害虫物种产生耐药性(第1节)。然而,由于在许多情况下耐药性的突然传播,它可能带来遗传变异的伴随侵蚀(第2节);这个过程被称为搭便车效应。在特定情况下,可变性的侵蚀程度取决于接触污染物的程度和分布、物种种群的遗传参数和抗性因素的遗传性质(第3节)。在许多情况下进行了遗传分析,害虫对杀虫剂的抗性似乎通常可归因于一个位点的基因。如果所调查的抗性病例是典型的,那么在某些情况下可能会出现搭便车效应,而在其他情况下则不会(第4节)。凝胶电泳技术的发展使得对物种群体的遗传变异性进行估计成为可能。因此,现在有可能直接调查污染是否在特定情况下侵蚀了遗传变异。这似乎只在一个案例中被调查过,尽管已经对250多个物种种群进行了遗传变异的估计,并且使用现有技术可以很容易地调查污染情况(第5节)。建议将遗传变异的电泳分析纳入污染监测计划,并在污染和控制环境中对同一个体进行污染浓度测量(第6节)。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Selective effects of insecticides on within-species variation: The lessons to be learnt when considering the environmental effects of pollutants

The use of insecticides has created environments which have favoured the development of resistance in many species that have been exposed to them. Exposure to insecticides has also brought about the development of resistance in some non-pest species (Section 1). However, because of the suddenness of the spread of resistance in many instances, it may bring about a concomitant erosion of genetic variability (Section 2); this process has been called the hitch-hiking effect. The extent of the erosion of variability that may be expected in a particular instance has been shown to depend on the extent and distribution of exposure to the pollutant, the genetic parameters of the species population and the genetic nature of the resistance factor (Section 3).

Genetic analyses have been carried out in a number of cases, and pest resistance to insecticides seems usually to be attributable to a gene at one locus. If the cases of resistance which have been investigated are typical, then hitch-hiking effects may be expected in some instances and not in others (Section 4).

The development of the technique of gel electrophoresis has enabled estimates to be made of the genetic variability of species populations. It is therefore now possible to investigate directly whether pollution has eroded genetic variability in particular instances. This seems to have been investigated in only one case, although estimates of genetic variability have been made for over 250 species populations and instances of pollution could easily be investigated using available techniques (Section 5).

It is suggested that electrophoretic analyses of genetic variability should be incorporated into pollution monitoring programmes and carried out in polluted and control environments on the same individuals for which measurements of pollutant concentrations are taken (Section 6).

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