4.7 Article

Diurnal variability of chlorinated polycyclic aromatic hydrocarbons in urban air, Japan

Journal

ATMOSPHERIC ENVIRONMENT
Volume 81, Issue -, Pages 84-91

Publisher

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.atmosenv.2013.08.044

Keywords

Chlorinated polycyclic aromatic hydrocarbons; PAHs; Urban air pollution; Diurnal variation; Emission sources

Funding

  1. Ministry of Education, Culture, Sports, Science and Technology [23310011]
  2. Environment Research and Technology Development Fund of the Ministry of the Environment, Japan [RFb-1103]
  3. Grants-in-Aid for Scientific Research [23310011] Funding Source: KAKEN

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Concentrations of 3- to 5-ring chlorinated polycyclic aromatic hydrocarbons (ClPAHs) and corresponding PAHs were quantified in 3-h integrated air samples, taken serially over 3-day periods in December 2009 (winter) and August 2010 (summer) in the urban area of Shizuoka, Japan. Twenty species of targeted CIPAHs were detected in both gas and particle phases throughout each campaign. Mean concentrations of total ClPAHs in the winter and summer campaigns were 133 +/- 53 pg m(-3) and 32 +/- 27 pg m(-3), respectively. Throughout the campaigns, diurnal variations of total ClPAHs concentrations did not have periodic fluctuation such as decreasing in daytime and increasing in nighttime, observed in PAHs. However, the mean concentrations of particulate ClPAHs trended to be slightly higher in nighttime than in daytime, but not for gaseous CIPAHs. Significant correlations were observed between the concentrations of total ClPAHs and total PAHs in particulate phase, but not in gaseous phase. In addition, for particulate phase, there were significant correlations between the concentrations of individual ClPAHs and corresponding parent PAHs, nitrate, and chlorine in summer, but not in winter. Considering these behaviors of ClPAHs in the air, the emission sources could have features of as follows: (i) specific emission sources emitted both CIPAHs and PAHs in particulate phase could be present in the area; (ii) particulate CIPAHs could be more strongly influenced by local sources and photochemical reactions rather than by transboundary air pollution; (iii) the possible sources could be combustion processes included biomass and fossil fuels. (C) 2013 Elsevier Ltd. All rights reserved.

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