Abstract

The chemical content of water-soluble organic carbon (WSOC) as a function of particle size was characterized in Little Rock, Arkansas in winter and spring 2013. The objectives of this study were to (i) compare the functional characteristics of coarse, fine and ultrafine WSOC and (ii) reconcile the sources of WSOC for periods when carbonaceous aerosol was the most abundant particulate component. The WSOC accounted for 5 % of particle mass for particles with δp > 0.96 μm and 10 % of particle mass for particles with δp < 0.96 μm. Non-exchangeable aliphatic (H–C), unsaturated aliphatic (H–C–C=), oxygenated saturated aliphatic (H–C–O), acetalic (O–CH–O) and aromatic (Ar–H) protons were determined by proton nuclear magnetic resonance (1H-NMR). The total non-exchangeable organic hydrogen concentrations varied from 4.1 ± 0.1 nmol m−3 for particles with 1.5 < δp < 3.0 μm to 73.9 ± 12.3 nmol m−3 for particles with δp < 0.49 μm. The molar H/C ratios varied from 0.48 ± 0.05 to 0.92 ± 0.09, which were comparable to those observed for combustion-related organic aerosol. The R–H was the most abundant group, representing about 45 % of measured total non-exchangeable organic hydrogen concentrations, followed by H–C–O (27 %) and H–C–C= (26 %). Levoglucosan, amines, ammonium and methanesulfonate were identified in NMR fingerprints of fine particles. Sucrose, fructose, glucose, formate and acetate were associated with coarse particles. These qualitative differences of 1H-NMR profiles for different particle sizes indicated the possible contribution of biological aerosols and a mixture of aliphatic and oxygenated compounds from biomass burning and traffic exhausts. The concurrent presence of ammonium and amines also suggested the presence of ammonium/aminium nitrate and sulfate secondary aerosol. The size-dependent origin of WSOC was further corroborated by the increasing δ13C abundance from −26.81 ± 0.18 ‰ for the smallest particles to −25.93 ± 0.31 ‰ for the largest particles and the relative distribution of the functional groups as compared to those previously observed for marine, biomass burning and secondary organic aerosol. The latter also allowed for the differentiation of urban combustion-related aerosol and biological particles. The five types of organic hydrogen accounted for the majority of WSOC for particles with δp > 3.0 μm and δp < 0.96 μm.

Highlights

  • Atmospheric aerosols affect climate directly by absorption and scattering of incoming solar radiation and indirectly through their involvement in cloud microphysical processes (Pöschl, 2005; Ghan and Schwartz, 2007)

  • Organic carbon (OC) was the predominant component of fine aerosol, accounting for 49 % of reconstructed PM2.5 mass, followed by secondary inorganic aerosol (40 %) and elemental carbon (EC) (7 %), which were comparable to those previously observed for the 2002–2010 period

  • Using 1H-NMR fingerprints, 13C isotopic analysis and molecular tracers, the sources of particulate water-soluble organic carbon (WSOC) were reconciled for specific functional organic groups

Read more

Summary

Introduction

Atmospheric aerosols affect climate directly by absorption and scattering of incoming solar radiation and indirectly through their involvement in cloud microphysical processes (Pöschl, 2005; Ghan and Schwartz, 2007). They influence atmospheric oxidative burden, visibility and human health (Sloane et al, 1991; Cho et al, 2005; Schlesinger et al, 2006). Organic carbon (OC) represents more than 40 % of aerosol mass in urban and continental areas, with the largest fraction of that being soluble in water, yet less than 20 % of that is chemically characterized (Putaud et al, 2004; Goldstein and Galbally, 2007). The incomplete characterization and the heterogeneity of organic aerosol limit our understanding of their fate and impacts

Objectives
Methods
Results
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call