U.S. Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, 109 T.W. Alexander Drive, Research Triangle Park, NC 27709, United States.
U.S. Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, 109 T.W. Alexander Drive, Research Triangle Park, NC 27709, United States.
Environ Int. 2014 Dec;73:304-11. doi: 10.1016/j.envint.2014.08.008. Epub 2014 Sep 3.
The U.S. EPA's SHEDS-Multimedia model was applied to enhance the understanding of children's exposures and doses to multiple pyrethroid pesticides, including major contributing chemicals and pathways. This paper presents combined dietary and residential exposure estimates and cumulative doses for seven commonly used pyrethroids, and comparisons of model evaluation results with NHANES biomarker data for 3-PBA and DCCA metabolites. Model input distributions were fit to publicly available pesticide usage survey data, NHANES, and other studies, then SHEDS-Multimedia was applied to estimate total pyrethroid exposures and doses for 3-5 year olds for one year variability simulations. For dose estimations we used a pharmacokinetic model and two approaches for simulating dermal absorption. SHEDS-Multimedia predictions compared well to NHANES biomarker data: ratios of 3-PBA observed data to SHEDS-Multimedia modeled results were 0.88, 0.51, 0.54 and 1.02 for mean, median, 95th, and 99th percentiles, respectively; for DCCA, the ratios were 0.82, 0.53, 0.56, and 0.94. Modeled time-averaged cumulative absorbed dose of the seven pyrethroids was 3.1 nmol/day (versus 8.4 nmol/day for adults) in the general population (residential pyrethroid use and non-use homes) and 6.7 nmol/day (versus 10.5 nmol/day for adults) in the simulated residential pyrethroid use population. For the general population, contributions to modeled cumulative dose by chemical were permethrin (60%), cypermethrin (22%), and cyfluthrin (16%); for residential use homes, contributions were cypermethrin (49%), permethrin (29%), and cyfluthrin (17%). The primary exposure route for 3-5 year olds in the simulated residential use population was non-dietary ingestion exposure; whereas for the simulated general population, dietary exposure was the primary exposure route. Below the 95th percentile, the major exposure pathway was dietary for the general population; non-dietary ingestion was the major pathway starting below the 70th percentile for the residential use population. The new dermal absorption methodology considering surface loading had some impact, but did not change the order of key pathways.
美国环保署的 SHEDS-Multimedia 模型被应用于增强对儿童接触和接触多种拟除虫菊酯农药的理解,包括主要贡献的化学物质和途径。本文提出了联合饮食和居住暴露估计值和 7 种常用拟除虫菊酯的累积剂量,并将模型评估结果与 NHANES 3-PBA 和 DCCA 代谢物的生物标志物数据进行了比较。模型输入分布符合公开的农药使用调查数据、NHANES 和其他研究,然后应用 SHEDS-Multimedia 来估计一年变异性模拟中 3-5 岁儿童的总拟除虫菊酯暴露和剂量。对于剂量估计,我们使用了一个药代动力学模型和两种模拟皮肤吸收的方法。SHEDS-Multimedia 的预测与 NHANES 生物标志物数据吻合较好:3-PBA 的观测数据与 SHEDS-Multimedia 模型结果的比值分别为 0.88、0.51、0.54 和 1.02,分别为平均值、中位数、95%和 99%百分位数;对于 DCCA,比值分别为 0.82、0.53、0.56 和 0.94。在一般人群(居住用拟除虫菊酯使用和不使用家庭)中,7 种拟除虫菊酯的模型平均累积吸收剂量为 3.1 nmol/天(成人 8.4 nmol/天),在模拟居住用拟除虫菊酯使用人群中为 6.7 nmol/天(成人 10.5 nmol/天)。对于一般人群,化学物质对模型累积剂量的贡献分别为氯菊酯(60%)、氯氰菊酯(22%)和氟氯氰菊酯(16%);对于居住用家庭,贡献分别为氯氰菊酯(49%)、氯菊酯(29%)和氟氯氰菊酯(17%)。在模拟居住用拟除虫菊酯使用人群中,3-5 岁儿童的主要暴露途径是非饮食摄入暴露;而对于模拟的一般人群,饮食暴露是主要暴露途径。在 95%百分位数以下,对于一般人群,主要暴露途径是饮食;对于居住用人群,从 70%百分位数以下开始,非饮食摄入是主要途径。考虑表面负荷的新皮肤吸收方法学有一定影响,但没有改变关键途径的顺序。