Abstract

Abstract. Air quality models that generate the concentrations of semi-volatile and other condensable organic compounds using an explicit reaction mechanism require estimates of the physical and thermodynamic properties of the compounds that affect gas/aerosol partitioning: vapour pressure (as a subcooled liquid), and activity coefficients in the aerosol phase. The model of Griffin, Kleeman and co-workers (e.g., Griffin et al., 2003; Kleeman et al., 1999) assumes that aerosol particles consist of an aqueous phase, containing inorganic electrolytes and soluble organic compounds, and a hydrophobic phase containing mainly primary hydrocarbon material. Thirty eight semi-volatile reaction products are grouped into ten surrogate species which partition between the gas phase and both phases in the aerosol. Activity coefficients of the organic compounds are calculated using UNIFAC. In a companion paper (Clegg et al., 2008) we examine the likely uncertainties in the vapour pressures of the semi-volatile compounds and their effects on partitioning over a range of atmospheric relative humidities. In this work a simulation for the South Coast Air Basin surrounding Los Angeles, using lower vapour pressures of the semi-volatile surrogate compounds consistent with estimated uncertainties in the boiling points on which they are based, yields a doubling of the predicted 24-h average secondary organic aerosol concentrations. The dependency of organic compound partitioning on the treatment of inorganic electrolytes in the air quality model, and the performance of this component of the model, are determined by analysing the results of a trajectory calculation using an extended version of the Aerosol Inorganics Model of Wexler and Clegg (2002). Simplifications are identified where substantial efficiency gains can be made, principally: the omission of dissociation of the organic acid surrogates; restriction of aerosol organic compounds to one of the two phases (aqueous or hydrophobic) where equilibrium calculations suggest partitioning strongly in either direction; a single calculation of activity coefficients of the organic compounds for simulations where they are determined by the presence of one component at high concentration in either phase (i.e., water in the aqueous phase, or a hydrocarbon surrogate compound P8 in the hydrophobic phase) and are therefore almost invariant. The implications of the results for the development of aerosol models are discussed.

Highlights

  • Atmospheric models of the inorganic components of aerosols, principally ammonium, sulphate, sea salt, components of wind blown dust, and nitrate, are relatively well established (e.g., Zhang et al, 2000; Jacobson, 1997; Nenes et al, 1998; Wexler and Clegg, 2002)

  • Aerosol particles in the UCD-Caltech Atmospheric Chemistry Mechanism (CACM) model can consist of 2 liquid phases: first, an aqueous phase containing water, inorganic ions, and some fraction of the secondary organic aerosol (SOA) surrogates and their dissociation products; second, a hydrophobic phase containing the primary hydrocarbons and the SOA surrogates which equilibrate between the two phases

  • Variations between models will be most apparent at low relative humidity both because differences between calculated water activity/concentration relationships of the solutes tend to be greatest at low RH, and especially because models may not predict the same amounts of inorganic solids to form causing large differences in predicted aerosol water content

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Summary

Introduction

Atmospheric models of the inorganic components of aerosols, principally ammonium, sulphate, sea salt, components of wind blown dust, and nitrate, are relatively well established (e.g., Zhang et al, 2000; Jacobson, 1997; Nenes et al, 1998; Wexler and Clegg, 2002). This work focuses on the impact on calculated gas/aerosol partitioning of uncertainties in some of the key elements of the thermodynamic treatment of both inorganic and organic aerosol compounds, including: activity coefficients, aerosol water content, solids formation, dissociation equilibria, and the treatment of groups of organic compounds using a reduced number of surrogate species. In steps (a) and (b) in Fig. 1 the partitioning of the primary and semi-volatile surrogate compounds between gas and aerosol phases is calculated for one or more aerosol size classes This process is driven by the (subcooled) liquid vapour pressures of the surrogate compounds and the associated enthalpies of vaporisation, and the activities in the aqueous and hydrophobic phases. In the section below we describe the thermodynamic models used and the chemical system treated, and summarise the calculation of solvent and solute activities and key uncertainties

The models
Chemical system
Solvent and solute activities
Vapour pressures
Comparisons
Inorganic component behaviour
Organic component behaviour
Partitioning of primary organic compounds
A2 A3 A4 A5 B1 B2 B3 B4 B5
Variations of subcooled vapour pressures po
Discussion
Organic components
Inorganic components
Future developments
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