Household air pollution and personal exposure risk of polycyclic aromatic hydrocarbons among rural residents in Shanxi, China

Polycyclic aromatic hydrocarbons (PAHs) are a group of pollutants of widespread concerns. Gaseous and size‐segregated particulate‐phase PAHs were collected in indoor and outdoor air in rural households. Personal exposure was measured and compared to the ingestion exposure. The average concentrations...

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Published inIndoor air Vol. 26; no. 2; pp. 246 - 258
Main Authors Chen, Y., Shen, G., Huang, Y., Zhang, Y., Han, Y., Wang, R., Shen, H., Su, S., Lin, N., Zhu, D., Pei, L., Zheng, X., Wu, J., Wang, X., Liu, W., Wong, M., Tao, S.
Format Journal Article
LanguageEnglish
Published England Blackwell Publishing Ltd 01.04.2016
Hindawi Limited
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Summary:Polycyclic aromatic hydrocarbons (PAHs) are a group of pollutants of widespread concerns. Gaseous and size‐segregated particulate‐phase PAHs were collected in indoor and outdoor air in rural households. Personal exposure was measured and compared to the ingestion exposure. The average concentrations of 28 parent PAHs and benzo(a)pyrene (BaP) were 9000 ± 8390 and 131 ± 236 ng/m3 for kitchen, 2590 ± 2270 and 43 ± 95 ng/m3 for living room, and 2800 ± 3890 and 1.6 ± 0.7 ng/m3 for outdoor air, respectively. The mass percent of high molecular weight (HMW) compounds with 5–6 rings contributed 1.3% to total 28 parent PAHs. Relatively higher fractions of HMW PAHs were found in indoor air compared to outdoor air. Majorities of particle‐bound PAHs were found in the finest PM0.25, and the highest levels of fine PM0.25‐bound PAHs were in the kitchen using peat and wood as energy sources. The 24‐h personal PAH exposure concentration was 2100 ± 1300 ng/m3. Considering energies, exposures to those using wood were the highest. The PAH inhalation exposure comprised up to about 30% in total PAH exposure through food ingestion and inhalation, and the population attributable fraction (PAF) for lung cancer in the region was 0.85%. The risks for inhaled and ingested intakes of PAHs were 1.0 × 10−5 and 1.1 × 10−5, respectively.
Bibliography:ArticleID:INA12204
National Natural Science Foundation of China - No. 41390240; No. 41161160559; No. 41130754
national 973 project - No. 2007CB5119001
istex:7697AC0B4E0EC7DA068CC48A3CCC89624C78C422
ark:/67375/WNG-TK3NKL85-7
Figure S1. The distributions of the 28 compounds in kitchen, living room, and ambient air (outdoor air) are shown as stacked bar chart presenting both particulate and gaseous phase PAHs in an increasing order of molecular weight. Figure S2. PAH composition profiles for samples collected in kitchens using different cooking energies (electricity, LPG, honeycomb briquettes, peat, and woods), including gaseous and particulate phases. Figure S3. The PAH composition profile measured using personal samplers. Means and standard errors are shown. Figure S4. The relationship between size percentage ratios and molecular weights for inhalation exposure. Table S1. The sample size in different sites (Songyan, Yixing, Liyang, and Pingsong) and energies (electricity, LPG, honeycomb briquette, peat, and wood) for personal samplers. Table S2. The sample size in different sites (Songyan, Yixing, and Liyang) and energies (electricity, LPG, Honeycomb briquette, peat, and wood) for stationary samples. Table S3. The measured average concentrations (ng/m3) of PAH28, PAH16, and BaP in kitchens and living rooms of individual households with different kind of cooking energies. Table S4. PAH concentration ratios of kitchen to outdoor (K/O) and living room to out door (L/O) for different energy households. Table S5. Relative potency factors of 27 pPAHs.
ObjectType-Article-1
SourceType-Scholarly Journals-1
ObjectType-Feature-2
content type line 23
ISSN:0905-6947
1600-0668
DOI:10.1111/ina.12204