Publication Cover
Journal of Environmental Science and Health, Part A
Toxic/Hazardous Substances and Environmental Engineering
Volume 51, 2016 - Issue 11
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ARTICLES

Concentrations of polycyclic aromatic hydrocarbons: Their potential health risks and sources at three non-urban sites in Japan

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Pages 884-899 | Received 01 Dec 2015, Published online: 17 Jun 2016
 

ABSTRACT

This investigation was undertaken to monitor particulate polycyclic aromatic hydrocarbons (PAHs) concentrations in order to determine their emission sources and potential human health risks in remote and rural areas of Japan. Seventeen PAHs in aerosol samples collected in remote (Kamihaya), coastal (Hiki) and inland (Higashi-Hiroshima) areas of Japan during 2013–2014 were analyzed using gas chromatography/mass spectrometry. Total PAH (Σ17PAH) concentrations in aerosol samples were in the range of 0.08–6.51 ng m−3, 0.09–4.74 ng m−3, and 0.21–6.53 ng m−3 at Kamihaya, Hiki, and Higashi-Hiroshima sites, with mean concentrations of 1.63, 1.18, and 2.43 ng m−3, respectively. Significant seasonal variation in concentrations occurred at Hiki and Higashi-Hiroshima, while no significant variation occurred at Kamihaya. Ambient air temperature greatly affected PAH concentrations in Higashi-Hiroshima, but had only moderate effects in Kamihaya and Hiki. Wind direction also influenced the concentrations of PAHs. Vehicle exhaust, industrial emissions, biomass combustion, and domestic heating and cooking were identified as the main PAH emission sources using principal component analysis. Backward trajectory calculations showed that domestically generated PAHs were significant in Kamihaya and Hiki, while in Higashi-Hiroshima concentrations were mainly influenced by long-range transport. The incremental lifetime lung cancer risk had values of 3.38 × 10−5 and 1.84 × 10−5 at Higashi-Hiroshima and Hiki, which are greater than the US EPA acceptable level (10−6). Typically, 5–6-ring PAHs contributed 95% to this overall health risk, of which benzo(a)pyrene was the largest contributor, followed by dibenz(a,h)anthracene at both residential sites. Clearly, stricter guidelines for PAHs need to be implemented at these sites to protect the population.

Acknowledgments

Staff at the Japan Agriculture (Kinan) and Mr. Katsumasa Oka collected air samples at Hiki and Kamihaya, respectively. We would like to thank the GIS lab of WWF-Pakistan for providing the study area map.

Funding

Funding was provided by the National Federation of Agricultural Cooperative Associations, Japan (Kinan Branch).

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