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Assessing contaminant sensitivity of endangered and threatened aquatic species: part I. Acute toxicity of five chemicals.

机译:评估濒危和受威胁水生物种的污染物敏感性:第一部分。五种化学品的急性毒性。

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Assessment of contaminant impacts to federally identified endangered, threatened and candidate, and state-identified endangered species (collectively referred to as "listed" species) requires understanding of a species' sensitivities to particular chemicals. The most direct approach would be to determine the sensitivity of a listed species to a particular contaminant or perturbation. An indirect approach for aquatic species would be application of toxicity data obtained from standard test procedures and species commonly used in laboratory toxicity tests. Common test species (fathead minnow, Pimephales promelas; sheepshead minnow, Cyprinodon variegatus; and rainbow trout, Oncorhynchus mykiss) and 17 listed or closely related species were tested in acute 96-hour water exposures with five chemicals (carbaryl, copper, 4-nonylphenol, pentachlorophenol, and permethrin) representing a broad range of toxic modes of action. No single species was the most sensitive to all chemicals. For the three standard test species evaluated, the rainbow trout was more sensitive than either the fathead minnow or sheepshead minnow and was equal to or more sensitive than listed and related species 81% of the time. To estimate an LC50 for a listed species, a factor of 0.63 can be applied to the geometric mean LC50 of rainbow trout toxicity data, and more conservative factors can be determined using variance estimates (0.46 based on 1 SD of the mean and 0.33 based on 2 SD of the mean). Additionally, a low- or no-acute effect concentration can be estimated by multiplying the respective LC50 by a factor of approximately 0.56, which supports the United States Environmental Protection Agency approach of multiplying the final acute value by 0.5 (division by 2). When captive or locally abundant populations of listed fish are available, consideration should be given to direct testing. When direct toxicity testing cannot be performed, approaches for developing protective measures using common test species toxicity data are available.
机译:评估污染物对联邦确定的濒危,威胁和候选以及州确定的濒危物种(统称为“所列”物种)的影响,需要了解该物种对特定化学物质的敏感性。最直接的方法是确定所列物种对特定污染物或微扰的敏感性。对于水生物种的间接方法是应用从标准测试程序和实验室毒性测试中常用的物种获得的毒性数据。常见的测试物种((鱼,Pimephales promelas,羊头min鱼,Cyprinodon variegatus和虹鳟鱼,Oncorhynchus mykiss)和17种列出或密切相关的物种在5种化学品(西维因,铜,4-壬基酚)的急性96小时水暴露中进行了测试。 (五氯苯酚和苄氯菊酯)代表了广泛的毒性作用方式。没有一个物种对所有化学物质最敏感。对于所评估的三个标准测试物种,虹鳟比the鱼或sheep鱼更敏感,并且在81%的时间内比所列和相关物种更敏感。要估算所列物种的LC50,可以将0.63的系数应用于虹鳟鱼毒性数据的几何平均LC50,可以使用方差估算值确定更保守的系数(0.46基于平均值的1 SD,0.33基于平均值)。平均值的2 SD)。此外,可以通过将各自的LC50乘以大约0.56的系数来估算低或非急性效应浓度,这支持美国环境保护署将最终急性值乘以0.5(除以2)的方法。当有圈养或当地丰富的所列鱼类种群时,应考虑进行直接检测。当无法进行直接毒性测试时,可以使用使用常见测试物种毒性数据制定保护措施的方法。

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