<p>Two hundred and sixty road dust samples collected from Xinjiang, China, were resuspended and analyzed for polycyclic aromatic hydrocarbons (PAHs) and their derivatives. The concentrations of ∑<sub>16</sub>PAHs, ∑<sub>18</sub>NPAHs and ∑<sub>5</sub>OPAHs (ng mg<sup>−1</sup>) in the road dust PM<sub>10</sub> ranged from 22.03 to 179.04, 0.34–3.14, and 0.95–17.56, with median values of 69.09, 1.14, and 4.37, respectively. Phe, Ace, Flt, 2N-Pyr, 9-FO, and ATO were the main substances found. The order of the median concentrations of ∑<sub>16</sub>PAHs in each city in the region was Altay &gt; Aksu &gt; Karamay &gt; Bole &gt; Kashgar &gt; Korla &gt; Tacheng &gt; Hami &gt; Turpan &gt; Wusu &gt; Hotan &gt; Kuitun &gt; Huyanghe &gt; Atushi. The order of the ∑<sub>18</sub>NPAHs concentrations in each city was Altay &gt; Karamay &gt; Hami &gt; Korla &gt; Bole &gt; Kashgar &gt; Wusu &gt; Tacheng &gt; Aksu &gt; Huyanghe &gt; Atushi &gt; Kuitun &gt; Hotan &gt; Turpan. The order of the ∑<sub>5</sub>OPAHs concentrations in each city was Altay &gt; Karamay &gt; Tacheng &gt; Kuitun &gt; Aksu &gt; Kashgar &gt; Korla &gt; Hami &gt; Wusu &gt; Bole &gt; Hotan &gt; Huyanghe &gt; Turpan &gt; Atushi. According to the diagnostic ratio and PMF results, four source factors were identified: biomass combustion (36.3%), coal combustion (39.0%), gasoline and diesel combustion (13.3%), and petroleum (11.4%). The total incremental lifetime cancer risks (TILCR) due to human exposure to road dust PAHs in Xinjiang were 8.2 × 10<sup>−6</sup> for children, 1.2 × 10<sup>−5</sup> for females, and 1.2 × 10<sup>−5</sup> for males.</p>

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Status, sources and health risk assessment of PAHs, NPAHs and OPAHs in road dust of Xinjiang, China

  • Xiawei Yang,
  • Yaqin Ji,
  • Bingbing Wang,
  • Jingwen Shi,
  • Wenju Xu,
  • Jiaofan Ma,
  • Ruixing Shen,
  • Yan Jiang

摘要

Two hundred and sixty road dust samples collected from Xinjiang, China, were resuspended and analyzed for polycyclic aromatic hydrocarbons (PAHs) and their derivatives. The concentrations of ∑16PAHs, ∑18NPAHs and ∑5OPAHs (ng mg−1) in the road dust PM10 ranged from 22.03 to 179.04, 0.34–3.14, and 0.95–17.56, with median values of 69.09, 1.14, and 4.37, respectively. Phe, Ace, Flt, 2N-Pyr, 9-FO, and ATO were the main substances found. The order of the median concentrations of ∑16PAHs in each city in the region was Altay > Aksu > Karamay > Bole > Kashgar > Korla > Tacheng > Hami > Turpan > Wusu > Hotan > Kuitun > Huyanghe > Atushi. The order of the ∑18NPAHs concentrations in each city was Altay > Karamay > Hami > Korla > Bole > Kashgar > Wusu > Tacheng > Aksu > Huyanghe > Atushi > Kuitun > Hotan > Turpan. The order of the ∑5OPAHs concentrations in each city was Altay > Karamay > Tacheng > Kuitun > Aksu > Kashgar > Korla > Hami > Wusu > Bole > Hotan > Huyanghe > Turpan > Atushi. According to the diagnostic ratio and PMF results, four source factors were identified: biomass combustion (36.3%), coal combustion (39.0%), gasoline and diesel combustion (13.3%), and petroleum (11.4%). The total incremental lifetime cancer risks (TILCR) due to human exposure to road dust PAHs in Xinjiang were 8.2 × 10−6 for children, 1.2 × 10−5 for females, and 1.2 × 10−5 for males.