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The use of ecotoxicological risk assessment in deriving maximum acceptable half‐lives of pesticides

机译:利用生态毒理学风险评估得出农药的最大可接受半衰期

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AbstractApproaches in ecological risk assessment are usually based on estimating the probability that organisms will be exposed to environmental concentrations of chemicals greater than some toxicological criterion (LC50, NOEC). Following this approach, quality standards for persistent chemicals in soil can be derived. For readily degradable chemicals emitted at intervals, the ecological risk can be related to the time taken for the chemical concentration to fall to a level causing no effect on most, e.g. 95, of the species. A formula is derived for the maximum acceptable half‐life, assuming a log–logistic distribution of species susceptibilities and a simple exponential decay of the chemical. It is also assumed that the pesticide is distributed homogeneously through the top 20 cm of the soil. A numerical example is elaborated for carbofuran, demonstrating that for a recommended dose applied to soil, the maximum half‐life should be 47 days, if the ecotoxicological protection level is to be reached within one year after a single application. This estimate may vary between 35 and 61 days, depending on the margins of uncertainty attached to ecotoxicological data. Complete recovery not only includes the disappearance of the chemical but also the recolonization of treated soils. The half‐life condition derived in this paper should therefore be considered as a minimum requ
机译:摘要生态风险评估的方法通常基于估计生物体暴露于高于某些毒理学标准(LC50,NOEC)的环境浓度的化学物质的概率。按照这种方法,可以得出土壤中持久性化学品的质量标准。对于每隔一段时间排放的易降解化学品,生态风险可能与化学品浓度下降到对大多数物种(例如95%)没有影响的水平所需的时间有关。推导了最大可接受半衰期的公式,假设物种易感性的对数-逻辑分布和化学品的简单指数衰减。还假设农药均匀地分布在土壤的顶部 20 厘米处。详细阐述了呋喃丹的数值实例,证明对于土壤施用的推荐剂量,如果在单次施用后一年内达到生态毒理学保护水平,则最长半衰期应为47天。这一估计可能在35至61天之间变化,具体取决于生态毒理学数据所附带的不确定性范围。完全恢复不仅包括化学品的消失,还包括处理过的土壤的重新定植。因此,本文中推导的半衰期条件应被视为最低要求

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