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Variation in the level of protection afforded to birds and crustaceans exposed to different pesticides under standard risk assessment procedures.

机译:在标准风险评估程序下,接触不同农药的鸟类和甲壳类动物的保护水平有所不同。

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摘要

First-tier risk assessment for pesticides is often based on the quotient of the toxicity divided by the predicted environmental concentration or dose. This ratio is compared to a fixed assessment factor (AF) to decide whether the pesticide is to be allowed on the market or whether further research is needed. Often, a high value (e.g., the 90th percentile) is assumed for the predicted environmental concentration, and the lowest available value is chosen to represent toxicity; yet, the real level of protection is not known. Therefore, it is also not known whether the first tier is conservative enough or too conservative. By using 2 large toxicity databases and assuming a log-logistic species sensitivity distribution for each pesticide, the percent of species not covered by the AF is estimated in the scenario, where exposure is at the maximum level allowable in the first tier. In the case of crustaceans, the median estimate of the fraction of species not covered by the AF of 100 in the first-tier scenario is 3.4%, on average, for 72 pesticides. In other words, on average, 3.4% of the crustacean species will be exposed above their median lethal concentration (LC50) and median lethal dose (LD50) value in 10% of receiving surface waters that receive the maximum allowable exposure to an individual pesticide. The estimated level of protection varies widely between pesticides. For 10% of the pesticides, the estimated fraction of species not covered is ≥10% (maximum = 41.4%). For 28% of the pesticides, 99.9% of the species will have the assumed level of protection. For birds, the median estimate of the fraction of species exposed above their median lethal dose for the first-tier scenario (AF = 10) is 3.0% on average, when the AF is applied to the lower of the toxicity values for the 2 standard test species. For 11% of the pesticides, the median estimate is ≥10% (maximum = 15.7%). When the AF is applied instead to the geometric mean of the toxicity values for the 2 standard species, the median estimate of the fraction of species not covered by the AF is increased to 7.4% on average; for 31% of the pesticides, this fraction is ≥10% (maximum = 33.4%). This variation in the level of protection should be considered when defining the assumptions, assessment factors, and decision criteria in regulatory risk assessment. Integr Environ Assess Manag 2011;7:459–465. © 2011 SETAC
机译:农药的一线风险评估通常基于毒性的商除以预测的环境浓度或剂量。将该比率与固定评估因子(AF)进行比较,以决定是否允许将农药投放市场或是否需要进一步研究。通常,对于预测的环境浓度,假定一个较高的值(例如,第90个百分位数),而选择最低的可用值来表示毒性。但是,真正的保护级别尚不清楚。因此,还不清楚第一层是否足够保守。通过使用2个大型毒性数据库并假设每种农药的对数物种敏感度分布,在这种情况下估算了AF未涵盖的物种百分比,在这种情况下,暴露水平处于第一层允许的最大水平。对于甲壳类动物,在第一线情景下,对于100种AF所未涵盖的物种比例的中位数估计值,对于72种农药而言,平均为3.4%。换句话说,在接受最大允许暴露于单个农药的接收地表水的10%中,平均有3.4%的甲壳类物种暴露于其致死率中位数(LC50)和致死率中位数(LD50)值以上。农药的估计保护水平差异很大。对于10%的农药,未覆盖物种的估计比例≥10%(最大(= 1.441.4%)。对于28%的农药,将有99.9%的物种具有假定的保护水平。对于禽类,当将AF应用于2种标准的毒性值中的较低者时,对于第一线情景(AF = 10),暴露于其致死剂量中位数以上的物种比例的中值估计平均为3.0%测试物种。对于11%的农药,中位估计值为≥10%(最大值= 15.7%)。当将AF应用于2个标准物种的毒性值的几何平均值时,AF未涵盖的物种比例的中位数估计值平均提高到7.4%;对于31%的农药,该比例≥10%(最大= 33.4%)。在定义监管风险评估中的假设,评估因素和决策标准时,应考虑保护级别的这种差异。 Integr环境评估管理杂志,2011年; 7:459–465。 ©2011 SETAC

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