Vehicles as outdoor BFR sources: Evidence from an investigation of BFR occurrence in road dust

被引:38
作者
Cao, Zhiguo [1 ,2 ]
Zhao, Leicheng [1 ]
Kuang, Jiangmeng [2 ,3 ]
Chen, Qiaoying [1 ]
Zhu, Guifen [1 ]
Zhang, Kunlun [2 ,3 ]
Wang, Shihua [1 ]
Wu, Peipei [1 ]
Zhang, Xin [1 ]
Wang, Xuefeng [1 ]
Harrad, Stuart [3 ]
Sun, Jianhui [1 ]
机构
[1] Henan Normal Univ, Sch Environm, Key Lab Yellow River & Huai River Water Environm, Minist Educ,Henan Key Lab Environm Pollut Control, Xinxiang 453007, Peoples R China
[2] Tsinghua Univ, Beijing Key Lab Emerging Organ Contaminants Contr, Sch Environm, Beijing 100084, Peoples R China
[3] Univ Birmingham, Sch Geog Earth & Environm Sci, Birmingham B15 2TT, W Midlands, England
基金
中国博士后科学基金; 中国国家自然科学基金;
关键词
BFRs; Road dust; Source; Exposure; Fate; POLYBROMINATED DIPHENYL ETHERS; BROMINATED FLAME RETARDANTS; HUMAN EXPOSURE; INDOOR DUST; DISTRIBUTION PATTERNS; DEPOSITED SEDIMENT; RISK-ASSESSMENT; UNITED-KINGDOM; PARTICLE-SIZE; HEAVY-METALS;
D O I
10.1016/j.chemosphere.2017.03.095
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The distribution of brominated flame retardants (BFRs) including Sigma 8PBDEs, DBDPE, BTBPE, EH-TBB, BEH-TEBP and PBEB in road dust (RD) collected in Xinxiang, China was characterized. Analysis of RD samples indicated that the BFR abundance declined as traffic density decreased, with total mean levels of 292, 184, 163, 104 and 70 ng g(-1) dust at sites from traffic intersections, main roads, collector streets, bypasses and parks, respectively. A possible explanation for this phenomenon is that the majority of BFRs may be emitted from the interior of vehicles via their ventilation systems. Of the 13 analyzed substances, BDE-209 and BEH-TEBP were the most abundant components in RD from Xinxiang. Similar amounts of Sigma BDEs excluding BDE-209 were found at different types of sampling sites, and thus, atmospheric deposition is also a probable source of BFRs in RD which can be subject to air transportation. The main PBDE sources were traced to commercial products including DE-71, Bromkal 79-8DE, Saytex 201E and Bromkal 82 DE mixtures. Our results confirm that the use of deca-BDE commercial mixture is a major source of PBDE contamination in RD. Risk assessment indicated the concentrations of BFRs in RD in this study do not constitute a non-cancer or cancer risk to humans through ingestion. Annual emission fluxes of.the commonly detected BFRs via RD in China were estimated to be up to 4980 kg year(-1). (C) 2017 Elsevier Ltd. All rights reserved.
引用
收藏
页码:29 / 36
页数:8
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