Abstract

Abstract. New primary and secondary organic aerosol modules have been added to PMCAMx, a three dimensional chemical transport model (CTM), for use with the SAPRC99 chemistry mechanism based on recent smog chamber studies. The new modelling framework is based on the volatility basis-set approach: both primary and secondary organic components are assumed to be semivolatile and photochemically reactive and are distributed in logarithmically spaced volatility bins. This new framework with the use of the new volatility basis parameters for low-NOx and high-NOx conditions tends to predict 4–6 times higher anthropogenic SOA concentrations than those predicted with the older generation of models. The resulting PMCAMx-2008 was applied in Mexico City Metropolitan Area (MCMA) for approximately a week during April 2003 during a period of very low regional biomass burning impact. The emission inventory, which uses as a starting point the MCMA 2004 official inventory, is modified and the primary organic aerosol (POA) emissions are distributed by volatility based on dilution experiments. The predicted organic aerosol (OA) concentrations peak in the center of Mexico City, reaching values above 40 μg m−3. The model predictions are compared with the results of the Positive Matrix Factorization (PMF) analysis of the Aerosol Mass Spectrometry (AMS) observations. The model reproduces both Hydrocarbon-like Organic Aerosol (HOA) and Oxygenated Organic Aerosol (OOA) concentrations and diurnal profiles. The small OA underprediction during the rush-hour periods and overprediction in the afternoon suggest potential improvements to the description of fresh primary organic emissions and the formation of the oxygenated organic aerosols, respectively, although they may also be due to errors in the simulation of dispersion and vertical mixing. However, the AMS OOA data are not specific enough to prove that the model reproduces the organic aerosol observations for the right reasons. Other combinations of contributions of primary and secondary organic aerosol production rates may lead to similar results. The model results strongly suggest that, during the simulated period, transport of OA from outside the city was a significant contributor to the observed OA levels. Future simulations should use a larger domain in order to test whether the regional OA can be predicted with current SOA parameterizations. Sensitivity tests indicate that the predicted OA concentration is especially sensitive to the volatility distribution of the emissions in the lower volatility bins.

Highlights

  • Anthropogenic air pollution is an increasingly serious problem for public health, global climate and ecosystems

  • This approach includes four species for V-secondary organic aerosol (SOA) produced from anthropogenic VOCs, assuming an average molecular weight of 150 g mol−1, and four additional species resulting from the oxidation of biogenic VOCs, assuming an average molecular weight of 180 g mol−1 and using the basis set for their effective saturation concentrations at 298 K: 1, 10, 100, 1000 μg m−3

  • The primary organic aerosol emissions were distributed among a set of volatility bins based on the fits to measured partitioning behaviour of diesel exhaust and wood smoke data

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Summary

Introduction

Anthropogenic air pollution is an increasingly serious problem for public health, global climate and ecosystems. Primary organic aerosol (POA) has been traditionally defined as the OA emitted into the atmosphere in particle form, e.g. from fossil fuel and biomass combustion, while secondary organic aerosol (SOA) is formed from gaseous precursors through gas-phase (Jacobson et al, 2000; Seinfeld et al, 2003; NARSTO, 2003), particle phase (Jang et al, 2002), or aqueous-phase reactions (Claeys et al, 2004; Blando, 2000) Due to their different origins and formation mechanisms, fresh POA and SOA usually have different chemical and microphysical properties (Mircea et al, 2002; Kerminen et al, 2000; Cruz et al, 1997; Kavouras et al, 2002; Zhang et al, 2005a; Aiken et al, 2008). The sensitivity of the proposed organic aerosol framework to the volatility distribution of the emissions is investigated

PMCAMx-2008 description
Partitioning of primary emissions
Secondary organic aerosol formation from VOCs
Chemical aging reactions
Volatility-resolved OA emission inventory
Model application
Predicted organic aerosol concentrations
Model performance evaluation for organic PM
Total organic aerosol mass
Local primary organics
Oxygenated organic aerosol
Sensitivity to changes in emissions and boundary conditions
Findings
Conclusions
Full Text
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