Abstract

Abstract. Hemispheric transport of air pollutants can have a significant impact on regional air quality, as well as on the effect of air pollutants on regional climate. An accurate representation of hemispheric transport in regional chemical transport models (CTMs) depends on the specification of the lateral boundary conditions (LBCs). This study focuses on the methodology for evaluating LBCs of two moderately long-lived trace gases, carbon monoxide (CO) and ozone (O3), for the European model domain and over a 7-year period, 2006–2012. The method is based on combining the use of satellite observations at the lateral boundary with the use of both satellite and in situ ground observations within the model domain. The LBCs are generated by the global European Monitoring and Evaluation Programme Meteorological Synthesizing Centre – West (EMEP MSC-W) model; they are evaluated at the lateral boundaries by comparison with satellite observations of the Terra-MOPITT (Measurements Of Pollution In The Troposphere) sensor (CO) and the Aura-OMI (Ozone Monitoring Instrument) sensor (O3). The LBCs from the global model lie well within the satellite uncertainties for both CO and O3. The biases increase below 700 hPa for both species. However, the satellite retrievals below this height are strongly influenced by the a priori data; hence, they are less reliable than at, e.g. 500 hPa. CO is, on average, underestimated by the global model, while O3 tends to be overestimated during winter, and underestimated during summer. A regional CTM is run with (a) the validated monthly climatological LBCs from the global model; (b) dynamical LBCs from the global model; and (c) constant LBCs based on in situ ground observations near the domain boundary. The results are validated against independent satellite retrievals from the Aqua-AIRS (Atmospheric InfraRed Sounder) sensor at 500 hPa, and against in situ ground observations from the Global Atmospheric Watch (GAW) network. It is found that (i) the use of LBCs from the global model gives reliable in-domain results for O3 and CO at 500 hPa. Taking AIRS retrievals as a reference, the use of these LBCs substantially improves spatial pattern correlations in the free troposphere as compared to results obtained with fixed LBCs based on ground observations. Also, the magnitude of the bias is reduced by the new LBCs for both trace gases. This demonstrates that the validation methodology based on using satellite observations at the domain boundary is sufficiently robust in the free troposphere. (ii) The impact of the LBCs on ground concentrations is significant only at locations in close proximity to the domain boundary. As the satellite data near the ground mainly reflect the a priori estimate used in the retrieval procedure, they are of little use for evaluating the effect of LBCs on ground concentrations. Rather, the evaluation of ground-level concentrations needs to rely on in situ ground observations. (iii) The improvements of dynamic over climatological LBCs become most apparent when using accumulated ozone over threshold 40 ppb (AOT40) as a metric. Also, when focusing on ground observations taken near the inflow boundary of the model domain, one finds that the use of dynamical LBCs yields a more accurate representation of the seasonal variation, as well as of the variability of the trace gas concentrations on shorter timescales.

Highlights

  • Hemispheric transport of aerosols and trace gases receives increasing attention owing to its impact on air quality, climate and visibility

  • This study aims to evaluate lateral boundary conditions (LBCs) from a global chemical transport model (CTM), the European Monitoring and Evaluation Programme (EMEP) MSC-W model by comparing them with satellite retrievals and by investigating the impact of the LBCs by implementing them into a regional chemical transport models (CTMs), the MATCH (Multi-scale Atmospheric Transport and CHemistry) model developed by the Swedish Meteorological and Hydrological Institute

  • The original EMEP model results are represented by grey dots, the smoothed EMEP results are shown as black solid lines, and the MOPITT retrievals and the a priori estimate are depicted as solid red and dashed blue lines, respectively

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Summary

Introduction

Hemispheric transport of aerosols and trace gases receives increasing attention owing to its impact on air quality, climate and visibility. Hemispheric transport can have a strong episodic impact on regional air quality (Fiore et al, 2002; Oltmans et al, 2006). Observational data from satellites of various tracers, such as carbon monoxide (CO) (Heald et al, 2003) and ozone (O3) (Zhang et al, 2008), corroborate that hemispheric transport of air pollutants can be important for regional and local air quality. While air quality studies traditionally have a strong focus on nearsurface concentration fields, climate effects of air pollution involve aerosols and radiatively active trace gases throughout the atmospheric column. In modelling systems that couple regional climate and regional air quality models (e.g. Thomas et al, 2015) hemispheric transport of pollutants is likely to play an important role

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