Abstract

The Korea-United States Air Quality (KORUS-AQ) field study was conducted during May–June 2016 to understand the factors controlling air quality in South Korea. Extensive aircraft and ground network observations from the campaign offer an opportunity to address issues in current air quality models and reduce model-observation disagreements. This study examines these issues using model evaluation against the KORUS-AQ observations and intercomparisons between models. Six regional and two global chemistry transport models using identical anthropogenic emissions participated in the model intercomparison study and were used to conduct air quality simulations focusing on ozone (O3), aerosols, and their precursors for the campaign. Using the KORUSv5 emissions inventory, which has been updated from KORUSv1, the models successfully reproduced observed nitrogen oxides (NOx) and volatile organic compounds mixing ratios in surface air, especially in the Seoul Metropolitan Area, but showed systematic low biases for carbon monoxide (CO), implying possible missing CO sources in the inventory in East Asia. Although the DC-8 aircraft-observed O3 precursor mixing ratios were well captured by the models, simulated O3 levels were lower than the observations in the free troposphere in part due to too low stratospheric O3 influxes, especially in regional models. During the campaign, the synoptic meteorology played an important role in determining the observed variability of PM2.5 (PM diameter ≤ 2.5 μm) concentrations in South Korea. The models successfully simulated the observed PM2.5 variability with significant inorganic sulfate-nitrate-ammonium aerosols contribution, but failed to reproduce that of organic aerosols, causing a large inter-model variability. From the model evaluation, we find that an ensemble of model results, incorporating individual models with differing strengths and weaknesses, performs better than most individual models at representing observed atmospheric compositions for the campaign. Ongoing model development and evaluation, in close collaboration with emissions inventory development, are needed to improve air quality forecasting.

Highlights

  • An international air quality field study, Korea-United States Air Quality (KORUS-AQ), which was jointly hosted by the Korean National Institute of Environmental Research (NIER) and U.S National Aeronautics and Space Administration (NASA), occurred in South Korea during May–June 2016, to understand the factors controlling air quality across urban, rural, and coastal interfaces (Crawford et al, n.d.)

  • Our intercomparison study focuses on model evaluation using extensive aircraft observations of major air pollutants and their precursors to address the formation of inorganic aerosols by gas/particle phase partitioning, chemical formation of organic aerosols, and several other issues raised from the campaign

  • Evaluation for aerosol compositions Variations in the aerosol chemical composition during the campaign were distinct among different synoptic patterns, which were examined by previous studies to explain the elevations in particulate matter (PM) loadings

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Summary

Introduction

Scientific findings and quantitative analyses of models’ capabilities in reproducing observations from the MICS-Asia initiative have been critical to improving our ability to predict air quality by contributing to advances in models (Carmichael and Ueda, 2008) These previous studies focused on the evaluation of models using observations mostly from a surface network (EANET). Our intercomparison study focuses on model evaluation using extensive aircraft observations of major air pollutants and their precursors to address the formation of inorganic aerosols by gas/particle phase partitioning, chemical formation of organic aerosols, and several other issues raised from the campaign. With the basic understanding of the campaign provided by observations, we here use an updated KORUS emissions inventory from Woo et al (n.d.) as an input to several air quality models to simulate gas and aerosol species and further evaluate the emissions, chemistry, and physical processes that affect model performance. Horizontal Resolution (Latitude  Longitude) Vertical Levels (

 9 km
Discussion
Conclusions
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