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Using Monte Carlo Analysis to Characterize the Uncertainty in Final Acute Values Derived From Aquatic Toxicity Data

机译:使用蒙特卡洛分析来表征由水生毒性数据得出的最终急性值的不确定性

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Many ambient water quality criteria established to protect aquatic life from acute toxicity are calculated using a procedure described in the US Environmental Protection Agency's "1985 Guidelines" (USEPA 1985). The procedure yields a final acute value (FAV) from acceptable median lethal or effective concentrations (LC50 or EC50, respectively) that is a single-point, deterministic estimate of the concentration of a chemical substance that will protect 95% of aquatic species from >50% mortality or other acute toxic effects. However, because of variation and uncertainty associated with toxicity test results, uncertainty in the estimated FAV exists that is not accounted for by the 1985 Guidelines procedure. Here, Monte Carlo analysis is used to characterize this uncertainty. The analysis uses Cu EC50 values adjusted for differences in test water chemistry obtained from USEPA's final freshwater Cu criteria guidance published in 2007. Additional Monte Carlo simulations illustrate Cu FAV distributions obtained using a subset of tested species and assuming fewer replicate tests. The deterministic procedure yields an FAV of 4.68 μg/Lforthe complete data set. By comparison, 3 replicate Monte Carlo simulations yielded mean FAVsof 4.66 μg/L. The 5th and 95th percentiles of the distribution of calculated FAVs were 4.14 μg/L and 5.20 μg/L, respectively. Reducing the number of tested genera from 27 to 8 (the minimum recommended by the 1985 Guidelines) and setting the number of tests per species equal to 3 yielded 5th and 95th percentiles of 1.22 μg/L and 6.18 μg/L, respectively, compared to a deterministic estimate of 2.80 μg/L. Results of this study indicate that Monte Carlo analysis can be used to improve the understanding and communication of uncertainty associated with water quality criteria derived from acute toxicity data using the 1985 Guidelines. This may benefit the development, revision, and application of these criteria in the future.
机译:为保护水生生物免受急性毒性而建立的许多环境水质标准是使用美国环境保护局的“ 1985年指南”(USEPA 1985年)中所述的程序进行计算的。该程序从可接受的中值致死浓度或有效浓度(分别为LC50或EC50)得出最终急性值(FAV),这是对95%的水生生物提供保护的化学物质浓度的单点确定性估计。 50%的死亡率或其他急性毒性作用。但是,由于毒性试验结果的变化和不确定性,存在估计的FAV中的不确定性,这是1985年指南程序无法解决的。在这里,使用蒙特卡洛分析来表征这种不确定性。该分析使用的铜EC50值已根据2007年美国环保局最终淡水铜标准指南中获得的测试水化学差异进行了调整。其他蒙特卡洛模拟说明了使用一部分被测物种并假设重复试验较少而获得的铜FAV分布。对于完整的数据集,确定性程序得出的FAV为4.68μg/ L。相比之下,3次重复蒙特卡洛模拟得出的平均FAV为4.66μg/ L。计算得出的FAV的分布的第5个百分点和第95个百分点分别为4.14μg/ L和5.20μg/ L。将测试属的数量从27个减少到8个(1985年指南建议的最小值),并将每个物种的测试数量设置为3个,则分别产生了1.22μg/ L和6.18μg/ L的第5个百分位数和第95个百分位数。确定性估计为2.80μg/ L。这项研究的结果表明,蒙特卡罗分析可用于改善与使用1985年指南从急性毒性数据得出的水质标准相关的不确定性的理解和交流。这将来可能会有利于这些标准的开发,修订和应用。

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