Abstract

Abstract. Secondary organic aerosol (SOA) plays a central role in air pollution and climate. However, the description of the sources and mechanisms leading to SOA is elusive despite decades of research. While stable isotope analysis is increasingly used to constrain sources of ambient aerosol, in many cases it is difficult to apply because neither the isotopic composition of aerosol precursors nor the fractionation of aerosol forming processes is well characterised. In this paper, SOA formation from ozonolysis of α-pinene – an important precursor and perhaps the best-known model system used in laboratory studies – was investigated using position-dependent and average determinations of 13C in α-pinene and advanced analysis of reaction products using thermal-desorption proton-transfer-reaction mass spectrometry (PTR-MS). The total carbon (TC) isotopic composition δ13C of the initial α-pinene was measured, and the δ13C of the specific carbon atom sites was determined using position-specific isotope analysis (PSIA). The PSIA analysis showed variations at individual positions from −6.9 to +10. 5 ‰ relative to the bulk composition. SOA was formed from α-pinene and ozone in a constant-flow chamber under dark, dry, and low-NOx conditions, with OH scavengers and in the absence of seed particles. The excess of ozone and long residence time in the flow chamber ensured that virtually all α-pinene had reacted. Product SOA was collected on two sequential quartz filters. The filters were analysed offline by heating them stepwise from 100 to 400 °C to desorb organic compounds that were (i) detected using PTR-MS for chemical analysis and to determine the O : C ratio, and (ii) converted to CO2 for 13C analysis. More than 400 ions in the mass range 39–800 Da were detected from the desorbed material and quantified using a PTR-MS. The largest amount desorbed at 150 °C. The O : C ratio of material from the front filter increased from 0.18 to 0.25 as the desorption temperature was raised from 100 to 250 °C. At temperatures above 250 °C, the O : C ratio of thermally desorbed material, presumably from oligomeric precursors, was constant. The observation of a number of components that occurred across the full range of desorption temperatures suggests that they are generated by thermal decomposition of oligomers. The isotopic composition of SOA was more or less independent of desorption temperature above 100 °C. TC analysis showed that SOA was enriched in 13C by 0.6–1.2 ‰ relative to the initial α-pinene. According to mass balance, gas-phase products will be depleted relative to the initial α-pinene. Accordingly, organic material on the back filters, which contain adsorbed gas-phase compounds, is depleted in 13C in TC by 0.7 ‰ relative to the initial α-pinene, and by 1.3 ‰ compared to SOA collected on the front filter. The observed difference in 13C between the gas and particle phases may arise from isotope-dependent changes in the branching ratios in the α-pinene + O3 reaction. Alternatively, some gas-phase products involve carbon atoms from highly enriched and depleted sites, as shown in the PSIA analysis, giving a non-kinetic origin to the observed fractionations. In either case, the present study suggests that the site-specific distribution of 13C in the source material itself governs the abundance of 13C in SOA.

Highlights

  • Secondary organic aerosol (SOA) is formed in the atmosphere by oxidation of volatile organic compounds (VOCs)

  • We argue that the observed isotope distribution in SOA is likely balanced by the opposite pattern in the gas-phase products, and that this pattern could be produced by site-specific enrichments in the starting material and current incomplete knowledge of the reaction mechanism alone, aside from whatever effects isotopic substitution may have on product branching ratios

  • The cloud condensation nuclei (CCN) activity of SOA generated in this study resembles literature data for α-pinene SOA generated in batch mode chambers (Fig. S3b)

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Summary

Introduction

Secondary organic aerosol (SOA) is formed in the atmosphere by oxidation of volatile organic compounds (VOCs). SOA contributes significantly to atmospheric aerosol and impacts climate, air quality, and health (Stocker et al, 2013; Hänninen et al, 2004; Dockery et al, 1993; Andreae and Crutzen, 1997). Despite their impacts the mechanisms of SOA formation and processing are poorly understood and significant discrepancies between model predictions and observations are common. The ability to distinguish individual sources, including marine aerosol (Turekian et al, 2003; Ceburnis et al, 2011) and biomass burning (Kirillova et al, 2013), by isotope measurements has been useful when it comes to source apportionment of ambient aerosol (e.g. Sakugawa and Kaplan, 1995; Narukawa et al, 2008; Turekian et al, 2003; Widory et al, 2004; Ho et al, 2006; Huang et al, 2006; Fisseha et al, 2009; Kirillova et al, 2013; Ceburnis et al, 2011; Fu et al, 2012; Miyazaki et al, 2012; O’Dowd et al, 2014; Masalaite et al, 2015)

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