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Evaluation of the vehicle contributions of metals to indoor environments

机译:评估车辆中金属对室内环境的影响

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A large number of diesel vehicles carrying gravel and sand shuttle back and forth every day on the major thoroughfares (Tai-16 and Tai-21) from Shinyi to Jiji in Nantou, Taiwan. A total of 10 stations along the major thoroughfares were selected as the exposure sites, whereas a small village located ~9 km from a main traffic route was selected as the control site. Outdoor and indoor aerosol samples were collected using high-volume samplers and Harvard samplers, respectively. The metal concentrations of outdoor and indoor PM 10 at the exposure sites were, respectively, higher than those at the control site. The plots between metal contents in the aerosols and road dust showed that diesel vehicles contributed significant amounts of metals to the outdoor and indoor aerosols at the exposure sites. Household dust samples along the roadside within 30 m of the main road in the small towns were collected using the wipe method. Based on the results of principal component analysis (PCA), three major components for household dust were identified: resuspended from road dust, brake wear and diesel emissions. Enrichment factors were applied to assess the contribution of pollution sources to household dust. These factors were calculated with respect to unpolluted river dust samples (EF river) and road dust (EF road). The differences between EF river and EF road could be mainly attributed to the effects of resuspension by passing vehicles. Approximately 72%, 68%, 68%, 73% and 86% of the vehicle-related metals Pb, Zn, Cu, Ni and Mo content, respectively, in household dust were the result of the resuspension of road dust by passing vehicles. The data of daily intakes of five metals (i.e., Fe, Pb, Cu, Ni and Mo) from inhalation and ingestion pathways showed that the doses from the ingestion pathway were much higher than those from the inhalation pathway.
机译:每天,从信义到南投的主要通道(Tai-16和Tai-21),大量载有砾石和沙子的柴油车来回穿梭。主要沿途共有10个车站被选为暴露地点,而距离主要交通路线约9公里的小村庄被选为控制地点。室外和室内气溶胶样品分别使用大容量采样器和哈佛采样器进行采集。暴露地点的室外和室内PM 10的金属浓度分别高于对照地点的金属浓度。气溶胶中金属含量与道路扬尘之间的关系图表明,柴油车辆在暴露地点向室外和室内气溶胶中贡献了大量金属。使用擦拭法收集小镇主干道30 m内路边的生活灰尘样品。根据主成分分析(PCA)的结果,确定了家庭灰尘的三个主要成分:从道路灰尘,刹车磨损和柴油排放中重新悬浮。富集因子用于评估污染源对家庭灰尘的贡献。这些因素是针对未污染的河尘样本(EF河)和道路尘土(EF道路)计算的。 EF河与EF道路之间的差异可能主要归因于过往车辆造成的停泊影响。家用粉尘中与车辆有关的金属Pb,Zn,Cu,Ni和Mo含量分别分别约为72%,68%,68%,73%和86%,这是由于过往车辆重新散布了道路粉尘。每天从吸入和摄入途径摄入的五种金属(即铁,铅,铜,镍和钼)的数据表明,从摄入途径摄入的剂量远高于从吸入途径摄入的剂量。

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