Abstract

Abstract. In order to better understand the particle size distribution of polycyclic aromatic hydrocarbons (PAHs) and their source contribution to human respiratory system, size-resolved PAHs have been studied in ambient aerosols at a megacity Shanghai site during a 1-year period (2012–2013). The results showed the PAHs had a bimodal distribution with one mode peak in the fine-particle size range (0.4–2.1 µm) and another mode peak in the coarse-particle size range (3.3–9.0 µm). Along with the increase in ring number of PAHs, the intensity of the fine-mode peak increased, while the coarse-mode peak decreased. Plotting of log(PAH / PM) against log(Dp) showed that all slope values were above −1, suggesting that multiple mechanisms (adsorption and absorption) controlled the particle size distribution of PAHs. The total deposition flux of PAHs in the respiratory tract was calculated as being 8.8 ± 2.0 ng h−1. The highest lifetime cancer risk (LCR) was estimated at 1.5 × 10−6, which exceeded the unit risk of 10−6. The LCR values presented here were mainly influenced by accumulation mode PAHs which came from biomass burning (24 %), coal combustion (25 %), and vehicular emission (27 %). The present study provides us with a mechanistic understanding of the particle size distribution of PAHs and their transport in the human respiratory system, which can help develop better source control strategies.

Highlights

  • Atmospheric polycyclic aromatic hydrocarbons (PAHs) are important contaminants in urban air because of their carcinogenic and mutagenic properties (Li et al, 2006; Garrido et al, 2014)

  • The present study provides us with a mechanistic understanding of the particle size distribution of PAHs and their transport in the human respiratory system, which can help develop better source control strategies

  • The daily PM2.5 concentration is 61.8 μg m−3, which is obviously higher than the annual national air quality standard of 10 (25) μg m−3 set by the World Health Organization (WHO, 2006)

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Summary

Introduction

Atmospheric PAHs are important contaminants in urban air because of their carcinogenic and mutagenic properties (Li et al, 2006; Garrido et al, 2014) They mainly result from incomplete combustion of carbon-containing materials and can partition between the gas and the particulate phase (Fernández et al, 2002; Hytönen et al, 2009; Shen et al, 2011). This partitioning process strongly depends on particle sizes, PAH species and temperature, and it affects PAH transport, deposition, and degradation as well as health impacts.

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