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Polychlorinated biphenyls contamination in urban soil of Shanghai: level, compositional profiles and source identification
Authors:Jiang Yufeng  Wang Xuetong  Zhu Kun  Wu Minghong  Sheng Guoying  Fu Jiamo
Institution:a School of Environmental & Municipal Engineering, Lanzhou Jiaotong University, Lanzhou 730070, China
b Institute of Environmental Pollution and Health, School of Environmental and Chemical Engineering, Shanghai University, Shanghai 200072, China
Abstract:Surface soil samples taken from 55 sampling sites at the urban areas of Shanghai were collected and analyzed for the occurrence of 144 polychlorinated biphenyls (PCBs) by GC-μECD. The results showed that totally 74 PCB congeners were identified and the mean concentration of total PCBs was 3057 ng kg−1 with a range of 232 to 11325 ng kg−1. Compared with the related reports, the level of PCBs contamination in this study was approximately equal to the global background value in soils, but higher than Chinese background for rural and urban soils. According to the compositional profiles of PCBs homologues, a higher proportion of low chlorinated (from tri-CBs to hexa-CBs) was observed. The results indicated that PCB15 + 13, PCB18, PCB28, PCB104 + 47 and PCB153 were the most dominant congeners among the identified PCBs. Through homologues analysis, cluster analysis and principal component analysis (PCA), it was found that PCBs were stretched from mixed local sources, and appeared to be mostly originated by Aroclor 1260- and 1254-like mixtures as well as some samples influenced by Aroclor 1232 and 1242. The correlation analysis showed the relatively good correlation among the PCB homologues and soil total organic carbon (TOC), suggesting important influence of soil TOC on PCBs contamination in soil matrix in Shanghai region. The toxic equivalency (TEQ) concentrations of these six dioxin-like PCBs detected in urban soil samples range from 2.71 to 24.9 pg kg−1-PCDDeq with a mean 8.18 pg kg−1-PCDDeq.
Keywords:Urban soil  PCBs  Homologues analysis  PCA  Shanghai
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