Abstract

Abstract. The ozonolysis of α-pinene has been investigated under dry and humid conditions in the temperature range of 243–303 K. The results provided new insight into the role of water and temperature in the degradation mechanism of α-pinene and in the formation of secondary organic aerosols (SOA). The SOA yields were higher at humid conditions than at dry conditions. The water induced gain was largest for the lowest temperatures investigated (243 and 253 K). The increase in the SOA yields was dominated by water (and temperature) effects on the organic product distribution, whilst physical uptake of water was negligible. This will be demonstrated for the example of pinonaldehyde (PA) which was formed as a major product in the humid experiments with total molar yields of 0.30±0.06 at 303 K and 0.15±0.03 at 243 K. In the dry experiments the molar yields of PA were only 0.07±0.02 at 303 K and 0.02±0.02 at 253 K. The observed partitioning of PA as a function of the SOA mass present at 303 K limited the effective vapour pressure of pure PA pPA0 to the range of 0.01–0.001 Pa, 3–4 orders of magnitude lower than literature values. The corresponding mass partitioning coefficient was determined to KPA=0.005±0.004 m3 μg−1 and the total mass yield αPAtotal=0.37±0.08. At 303 K PA preferably stayed in the gas-phase, whereas at 253 K and 243 K it exclusively partitioned into the particulate phase. PA could thus account at least for half of the water induced gain in SOA mass at 253 K. The corresponding effect was negligible at 303 K because the PA preferably remained in the gas-phase. The yield of OH radicals, which were produced in the ozonolysis, was indirectly determined by means of the yield of cyclohexanone formed in the reaction of OH radicals with cyclohexane. OH yields of the α-pinene ozonolysis were determined to 0.67±0.17 for humid and 0.54±0.13 for dry conditions at 303 K, indicating a water dependent path of OH radical formation. For 253 and 243 K OH yields could be estimated to 0.5 with no significant difference between the dry and humid experiments. This is the first clear indication for OH radical formation by α-pinene ozonolysis at such low temperatures.

Highlights

  • Ozonolysis of large unsaturated compounds, such as monoterpenes (C10H16) has been and still is of concern when it comes to formation of atmospheric secondary organic aerosols (SOA) (Hallquist et al, 2009; Kanakidou et al, 2005; Went, 1960)

  • The SOA concentration produced from α-pinene ozonolysis was measured at several temperatures in the presence and absence of water vapour

  • The CE/ESI-ITMS analysis of the front and back filters sampled during an ozonolysis experiment at 303 K under humid conditions leads to a lower estimate of the pinonic acid molar yield of 0.08

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Summary

Introduction

Ozonolysis of large unsaturated compounds, such as monoterpenes (C10H16) has been and still is of concern when it comes to formation of atmospheric secondary organic aerosols (SOA) (Hallquist et al, 2009; Kanakidou et al, 2005; Went, 1960). Previous studies have presented positive, negative and neutral dependence of pinonaldehyde production on water concentration (Baker et al, 2001; Berndt et al, 2003; Bonn et al, 2002; Warscheid and Hoffmann, 2001). These discrepancies may be explained by experimental conditions and will be discussed later with respect to the results presented here. The focus of this paper is on the interplay of humidity and temperature in the formation and partitioning of pinonaldehyde in relation to other simultaneous observations such as aerosol water content, OH radical and SOA production. The presented results are used to further improve the understanding of the mechanism of the ozonolysis of α-pinene with emphasis on its dependence on water and temperature

Experimental
SOA mass
Water absorption
Pinonaldehyde
OH radical formation
Implication for degradation mechanism of α-pinene
Summary and conclusions
Full Text
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