Abstract

Abstract. We present a novel analytical approach to measure the chemical composition of organic aerosol. The new instrument combines proton-transfer-reaction mass-spectrometry (PTR-MS) with a collection-thermal-desorption aerosol sampling technique. For secondary organic aerosol produced from the reaction of ozone with isoprenoids in a laboratory reactor, the TD-PTR-MS instrument detected typically 80% of the mass that was measured with a scanning mobility particle sizer (SMPS). The first field deployment of the instrument was the EUCAARI-IOP campaign at the CESAR tall tower site in the Netherlands. For masses with low background values (~30% of all masses) the detection limit of aerosol compounds was below 0.2 ng/m3 which corresponds to a sampled compound mass of 35 pg. Comparison of thermograms from ambient samples and from chamber-derived secondary organic aerosol shows that, in general, organic compounds from ambient aerosol samples desorb at much higher temperatures than chamber samples. This suggests that chamber aerosol is not a good surrogate for ambient aerosol and therefore caution is advised when extrapolating results from chamber experiments to ambient conditions.

Highlights

  • Organic aerosol (OA) sources in the global atmosphere are enormously uncertain

  • A compilation of aerosol mass spectrometer (AMS) field observations in the northern hemisphere shows that approximately 95% of the OA mass in the remote continental boundary layer has a characteristic electron-impact ionization mass spectrum dubbed “oxidized organic aerosol” (OOA), with urban environments containing about 67% OOA (Zhang et al, 2007)

  • We report first results obtained from chamber produced secondary organic aerosol (SOA) from ozonolysis of isoprenoids and from ambient aerosol as measured during the EUCAARI-IOP campaign in Cabauw, Netherlands, in May 2008

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Summary

Introduction

Organic aerosol (OA) sources in the global atmosphere are enormously uncertain. While state-of-the-art models predict total organic aerosol formation rates of 12–70 Tg yr−1 (Hallquist et al, 2009; Kanakidou et al, 2005), alternative budgeting approaches indicate significantly higher OA production. Field observations consistently reveal 3–10 times more organic aerosol than predicted by models (Heald et al, 2005; Volkamer et al, 2006), while top-down estimates suggest between 60 and 330 TgC yr−1 (120–660 Tg OA yr−1) (Goldstein and Galbally, 2007), again several times higher than global model predictions The search for this “missing” source of OA has become a key research topic, with hypotheses including higher secondary organic aerosol (SOA) yields from volatile organic precursors such as isoprene (Kroll et al, 2006; Paulot et al, 2009) or toluene (Hildebrandt et al, 2009; Ng et al, 2007), heterogeneous uptake of glyoxal (Kroll et al, 2005; Volkamer et al, 2007), aqueous photochemistry (Ervens et al, 2008), or oxidation of low vaporpressure “intermediate volatility organics” (IVOC) (Donahue et al, 2006; Grieshop et al, 2008; Robinson et al, 2007). We report first results obtained from chamber produced secondary organic aerosol (SOA) from ozonolysis of isoprenoids and from ambient aerosol as measured during the EUCAARI-IOP campaign in Cabauw, Netherlands, in May 2008

The TD-PTR-MS instrument
Smog chamber measurements
Information obtained from the thermograms
Conclusions
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