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接触铬酸铜砷酸盐(CCA)处理过的儿童游乐设施和平台的儿童的概率性砷暴露评估,第2部分:敏感性和不确定性分析。

A probabilistic arsenic exposure assessment for children who contact chromated copper arsenate (CCA)-treated playsets and decks, Part 2: Sensitivity and uncertainty analyses.

作者信息

Xue Jianping, Zartarian Valerie G, Ozkaynak Halûk, Dang Winston, Glen Graham, Smith Luther, Stallings Casson

机构信息

U.S. Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, Research Triangle Park, NC, USA.

出版信息

Risk Anal. 2006 Apr;26(2):533-41. doi: 10.1111/j.1539-6924.2006.00748.x.

Abstract

A probabilistic model (SHEDS-Wood) was developed to examine children's exposure and dose to chromated copper arsenate (CCA)-treated wood, as described in Part 1 of this two-part article. This Part 2 article discusses sensitivity and uncertainty analyses conducted to assess the key model inputs and areas of needed research for children's exposure to CCA-treated playsets and decks. The following types of analyses were conducted: (1) sensitivity analyses using a percentile scaling approach and multiple stepwise regression; and (2) uncertainty analyses using the bootstrap and two-stage Monte Carlo techniques. The five most important variables, based on both sensitivity and uncertainty analyses, were: wood surface residue-to-skin transfer efficiency; wood surface residue levels; fraction of hand surface area mouthed per mouthing event; average fraction of nonresidential outdoor time a child plays on/around CCA-treated public playsets; and frequency of hand washing. In general, there was a factor of 8 for the 5th and 95th percentiles and a factor of 4 for the 50th percentile in the uncertainty of predicted population dose estimates due to parameter uncertainty. Data were available for most of the key model inputs identified with sensitivity and uncertainty analyses; however, there were few or no data for some key inputs. To evaluate and improve the accuracy of model results, future measurement studies should obtain longitudinal time-activity diary information on children, spatial and temporal measurements of residue and soil concentrations on or near CCA-treated playsets and decks, and key exposure factors. Future studies should also address other sources of uncertainty in addition to parameter uncertainty, such as scenario and model uncertainty.

摘要

如这篇分两部分的文章第一部分所述,已开发出一种概率模型(SHEDS-Wood)来研究儿童对铬酸铜砷酸盐(CCA)处理过的木材的暴露情况和剂量。本文第二部分讨论了为评估儿童接触经CCA处理的游乐设施和平台的关键模型输入以及所需研究领域而进行的敏感性和不确定性分析。进行了以下类型的分析:(1)使用百分位数缩放方法和多元逐步回归的敏感性分析;(2)使用自助法和两阶段蒙特卡罗技术的不确定性分析。基于敏感性和不确定性分析,五个最重要的变量是:木材表面残留物到皮肤的转移效率;木材表面残留物水平;每次啃咬事件中接触口腔的手部表面积比例;儿童在经CCA处理的公共游乐设施上/周围玩耍的非居住户外时间的平均比例;以及洗手频率。一般来说,由于参数不确定性,预测人群剂量估计的不确定性中,第5和第95百分位数相差8倍,第50百分位数相差4倍。对于通过敏感性和不确定性分析确定的大多数关键模型输入都有数据;然而,一些关键输入的数据很少或没有。为了评估和提高模型结果的准确性,未来的测量研究应获取有关儿童的纵向时间活动日记信息、经CCA处理的游乐设施和平台上或附近残留物和土壤浓度的空间和时间测量数据以及关键暴露因素。未来的研究除了参数不确定性之外,还应解决其他不确定性来源,例如情景和模型不确定性。

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