Abstract

Abstract. This study investigates the concentration, cloud condensation nuclei (CCN) activity and hygroscopic properties of particles influenced by biomass burning in the eastern Mediterranean and their impacts on cloud droplet formation. Air masses sampled were subject to a range of atmospheric processing (several hours up to 3 days). Values of the hygroscopicity parameter, κ, were derived from CCN measurements and a Hygroscopic Tandem Differential Mobility Analyzer (HTDMA). An Aerosol Chemical Speciation Monitor (ACSM) was also used to determine the chemical composition and mass concentration of non-refractory components of the submicron aerosol fraction. During fire events, the increased organic content (and lower inorganic fraction) of the aerosol decreases the values of κ, for all particle sizes. Particle sizes smaller than 80 nm exhibited considerable chemical dispersion (where hygroscopicity varied up to 100 % for particles of same size); larger particles, however, exhibited considerably less dispersion owing to the effects of condensational growth and cloud processing. ACSM measurements indicate that the bulk composition reflects the hygroscopicity and chemical nature of the largest particles (having a diameter of ∼ 100 nm at dry conditions) sampled. Based on positive matrix factorization (PMF) analysis of the organic ACSM spectra, CCN concentrations follow a similar trend as the biomass-burning organic aerosol (BBOA) component, with the former being enhanced between 65 and 150 % (for supersaturations ranging between 0.2 and 0.7 %) with the arrival of the smoke plumes. Using multilinear regression of the PMF factors (BBOA, OOA-BB and OOA) and the observed hygroscopicity parameter, the inferred hygroscopicity of the oxygenated organic aerosol components is determined. We find that the transformation of freshly emitted biomass burning (BBOA) to more oxidized organic aerosol (OOA-BB) can result in a 2-fold increase of the inferred organic hygroscopicity; about 10 % of the total aerosol hygroscopicity is related to the two biomass-burning components (BBOA and OOA-BB), which in turn contribute almost 35 % to the fine-particle organic water of the aerosol. Observation-derived calculations of the cloud droplet concentrations that develop for typical boundary layer cloud conditions suggest that biomass burning increases droplet number, on average by 8.5 %. The strongly sublinear response of clouds to biomass-burning (BB) influences is a result of strong competition of CCN for water vapor, which results in very low maximum supersaturation (0.08 % on average). Attributing droplet number variations to the total aerosol number and the chemical composition variations shows that the importance of chemical composition increases with distance, contributing up to 25 % of the total droplet variability. Therefore, although BB may strongly elevate CCN numbers, the impact on droplet number is limited by water vapor availability and depends on the aerosol particle concentration levels associated with the background.

Highlights

  • Biomass burning (BB) is a major source of atmospheric aerosols (Andreae et al, 2004)

  • The organic aerosol derived from the ageing of the biomass-burning aerosol (OOA-BB) identified for all events had a similar profile, regardless of the biomass-burning organic aerosol (BBOA) it was derived from (Bougiatioti et al, 2014)

  • To quantify the direct influence of biomass burning to particle and cloud condensation nuclei (CCN) number concentrations, we studied the concentration of the BBOA component, identified by positive matrix factorization (PMF) analysis of the Aerosol Chemical Speciation Monitor (ACSM) mass spectra (Bougiatioti et al, 2014)

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Summary

Introduction

Biomass burning (BB) is a major source of atmospheric aerosols (Andreae et al, 2004). In the eastern Mediterranean, up to one-third of the dry submicron aerosol mass during the summer period consists of highly oxidized organic compounds (Hildebrandt et al, 2010). During July– September, biomass-burning aerosol originates from longrange transport from southern Europe and countries surrounding the Black Sea (Sciare et al, 2008). Bougiatioti et al (2014) showed that of the total organic aerosol (OA), about 20 % is freshly emitted biomass-burning organic aerosol (BBOA), 30 % is oxidized, processed OA originating from BBOA (BB-OOA), and the remaining 50 % is highly oxidized aerosol that results from extensive atmospheric ageing. In terms of organic mass, during time periods of high biomass-burning activity, at least 50 % of the aerosol can be attributed to BB emissions. LWC is a prime modulator of aerosol direct radiative forcing (e.g., Pilinis et al, 1995), and by promoting secondary aerosol formation it can influence aerosol mass and number that impact both the direct and indirect effect of aerosols (Kanakidou et al, 2005)

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