Abstract
Abstract. This study presents the first modeling estimates of the potential effect of gas- and particle-phase organic photolysis reactions on the formation and lifetime of secondary organic aerosols (SOAs). Typically only photolysis of smaller organic molecules (e.g., formaldehyde) for which explicit data exist is included in chemistry–climate models. Here, we specifically examine the photolysis of larger molecules that actively partition between the gas and particle phases. The chemical mechanism generator GECKO-A is used to explicitly model SOA formation from α-pinene, toluene, and C12 and C16 n-alkane reactions with OH at low and high NOx. Simulations are conducted for typical mid-latitude conditions and a solar zenith angle of 45° (permanent daylight). The results show that after 4 days of chemical aging under those conditions (equivalent to 8 days in the summer mid-latitudes), gas-phase photolysis leads to a moderate decrease in SOA yields, i.e., ~15 % (low NOx) to ~45 % (high NOx) for α-pinene, ~15 % for toluene, ~25 % for C12 n-alkane, and ~10 % for C16 n-alkane. The small effect of gas-phase photolysis on low-volatility n-alkanes such as C16 n-alkane is due to the rapid partitioning of early-generation products to the particle phase, where they are protected from gas-phase photolysis. Minor changes are found in the volatility distribution of organic products and in oxygen to carbon ratios. The decrease in SOA mass is increasingly more important after a day of chemical processing, suggesting that most laboratory experiments are likely too short to quantify the effect of gas-phase photolysis on SOA yields. Our results also suggest that many molecules containing chromophores are preferentially partitioned into the particle phase before they can be photolyzed in the gas phase. Given the growing experimental evidence that these molecules can undergo in-particle photolysis, we performed sensitivity simulations using an empirically estimated SOA photolysis rate of JSOA = 4 × 10−4 JNO2. Modeling results indicate that this photolytic loss rate would decrease SOA mass by 40–60 % for most species after 10 days of equivalent atmospheric aging at mid-latitudes in the summer. It should be noted that in our simulations we do not consider in-particle or aqueous-phase reactions which could modify the chemical composition of the particle and thus the quantity of photolabile species. The atmospheric implications of our results are significant for both the SOA global distribution and lifetime. GEOS-Chem global model results suggest that particle-phase photolytic reactions could be an important loss process for SOA in the atmosphere, removing aerosols from the troposphere on timescales of less than 7 days that are comparable to wet deposition.
Highlights
Secondary organic aerosols (SOAs) are ubiquitous atmospheric constituents formed by photochemical oxidation of anthropogenic and biogenic hydrocarbons that can lead to adverse health effects (Fann et al, 2012) and radiative forcing of climate (Boucher et al, 2013)
We investigated the sensitivity of secondary organic aerosols (SOAs) formation and aging in the atmosphere to gas-phase and inparticle photolysis reactions of organic compounds that actively partition between gas and particle phases
We apply the explicit chemistry model GECKO-A to simulate SOA formation from OH oxidation of α-pinene, toluene, and C12 and C16 n-alkane precursors, and to explore the sensitivity of this formation to gas-phase photolysis explicitly calculated in the model
Summary
Secondary organic aerosols (SOAs) are ubiquitous atmospheric constituents formed by photochemical oxidation of anthropogenic and biogenic hydrocarbons that can lead to adverse health effects (Fann et al, 2012) and radiative forcing of climate (Boucher et al, 2013). Their atmospheric burden and lifetime are highly uncertain due to our limited understanding of processes controlling their formation, aging and removal in the atmosphere. Unlike OH reactions that mainly lead to addition of more functional groups, photolysis mainly fragments molecules into smaller and more volatile compounds, significantly modifying SOA composition and properties during atmospheric aging
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