Abstract

Size-segregated aerosol samples were collected with a low-pressure impactor (LPI) at urban, roadside and rural sites in winter in Beijing. The size distribution of Polycyclic Aromatic Hydrocarbons (PAHs), organic carbon (OC) and elemental carbon (EC) were measured and this study focused on their size distributions and relationships of PAH to OC/EC. All PAHs show uni-modal at the accumulation mode (0.1–1.8 μm) and almost all PAHs are associated with fine particles. The absence of PAHs in the nucleus mode contributes to the coagulation under the condition of high concentration of the accumulation mode particles. The absence of PAHs in the coarse mode was probably attributed to the low temperature that restrained the redistribution of PAHs from the accumulation mode to the coarse mode. Flu(fluoranthene) and Pyr(pyrene, 4-ring) were the most abundant particulate PAHs ; however, IcdP(indeno[1,2,3-cd]pyrene) and BghiP(benzo[ghi]perylene, 6-ring) were rather low. Diagnostic ratios show vehicle and coal burning were the major sources of PAHs in winter. Ratios at rural site are obviously different from those found at roadside and urban sites. Lower value of OC/EC in the rural area than that in the urban area was probably resulted from coal burning prevailed in the rural area. OC1 and OC2 exhibit uni-mode distribution similar to their particle surface area distribution indicating their existence on particles by adsorption. OC3 and OC4 show bi-mode distribution. Grinding of biomass debris can be a probable source of OC3 and OC4 in the coarse mode. EC1 is mostly from the pyrolysis of OC; however, both the natural and anthropogenic emissions contribute to EC2. The correlation between size-segregated PAHs and carbonaceous component is also discussed to identify their sources.

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