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Population Consequences of Fipronil and Degradates to Copepods at Field Concentrations: An Integration of Life Cycle Testing with Leslie Matrix Population Modeling

机译:氟虫腈的种群结果以及在现场浓度下降解为Co足类动物的研究:生命周期测试与莱斯利矩阵种群建模的集成

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The predominant data used in ecological risk assessment today are individual-based rather than population-based; yet environmental policies are usually designed to protect populations of threatened species or communities. Most current methods in ecotoxicology are limited by largely logistic/technology-driven requirements that yield data for a relatively small number of test species and end points that focus on acute lethality or sublethal nonproduction-based parameters (e.g., biomarkers, mutagenesis, genetic change, physiological condition). A contrasting example is presented here showing the predictive ability of meiobenthos-based full life cycle toxicity testing to extrapolate multi-generational effects of chemicals on variables of import to population growth and maintenance. Less than 24-h-old larvae of a meiobenthic copepod were reared individually in 96-well microplate exposures to parent and degradates of the phenylpyrazole insecticide fipronil. Survival, development rates, sex ratio change, fertility, fecundity, and hatching success were tracked daily for 32 d through mating and production of three broods in spiked seawater. These data were then inserted in a Leslie (Lefkovitch) matrix stage-based population growth model to predict relative rates of population increase U) and changes in net population growth with time and toxicant concentration. Field-reported test concentrations produced strong reproductive (52-88%) and net production (40-80%) depressions for parent (at 0.25 and 0.5 μg/L), desthionyl (0.25 and 0.5μg/L), and sulfide (0.15μg/L) moieties as compared to controls. Spiked sediment exposures of 65-300 ng of fipronil/g of dry sediment yielded significantly reduced production rates per female that were 67-50% of control production. The consistent reproductively linked impacts of fipronil and its degradation products at the population maintenance levels suggest risks to sediment-dwelling crustaceans at concentrations well below noneffects for most aquatic test species based on risk assessment data from primarily acute and sub-life cycle toxicity tests.
机译:今天,生态风险评估中使用的主要数据是基于个人的,而不是基于人口的。然而,环境政策通常旨在保护受威胁物种或社区的种群。当前大多数生态毒理学方法受到后勤/技术驱动的要求的限制,这些要求会产生相对较少数量的测试物种的数据以及关注急性致死性或亚致死性非生产性参数(例如生物标记,诱变,遗传变化,生理状况)。此处提供了一个对比示例,该示例显示了基于甲基苯甲醚的全生命周期毒性测试的预测能力,可以推断化学物质对人口增长和维持的进口变量的多代影响。在96孔微孔板暴露于母体并降解苯基吡唑杀虫剂氟虫腈的情况下,分别饲养了不足24小时的中足co足类幼虫。每天追踪32天,通过在加标的海水中交配和繁殖三个亲鱼来存活,发育,改变性别,生育力,繁殖力和孵化成功率。然后将这些数据插入基于Leslie(Lefkovitch)矩阵阶段的人口增长模型中,以预测人口相对增长率(U)以及净人口增长随时间和毒物浓度的变化。现场报告的测试浓度对母体(分别为0.25和0.5μg/ L),去硫酰(分别为0.25和0.5μg/ L)和硫化物(0.15)产生强烈的生殖(52-88%)和净产量(40-80%)抑制与对照相比,微克/升)部分。刺突的沉积物暴露于65-300 ng的氟虫腈/ g干沉积物,导致每只雌性的生产率显着降低,为对照产量的67-50%。氟虫腈及其降解产物在种群维持水平上的一致的生殖联系影响表明,根据主要来自急性和亚生命周期毒性试验的风险评估数据,对于大多数水生试验物种而言,浓度远低于无影响的底栖甲壳类动物的风险。

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