Abstract

Abstract. Land transport is an important emission source of nitrogen oxides, carbon monoxide, and volatile organic compounds. The emissions of nitrogen oxides affect air quality directly. Further, all of these emissions serve as a precursor for the formation of tropospheric ozone, thus leading to an indirect influence on air quality. In addition, ozone is radiatively active and its increase leads to a positive radiative forcing. Due to the strong non-linearity of the ozone chemistry, the contribution of emission sources to ozone cannot be calculated or measured directly. Instead, atmospheric chemistry models equipped with specific source attribution methods (e.g. tagging methods) are required. In this study we investigate the contribution of land transport emissions to ozone and ozone precursors using the MECO(n) model system (MESSy-fied ECHAM and COSMO models nested n times). This model system couples a global and a regional chemistry climate model and is equipped with a tagging diagnostic. We investigate the combined effect of long-range-transported ozone and ozone which is produced by European emissions by applying the tagging diagnostic simultaneously and consistently on the global and regional scale. We performed two simulations each covering 3 years with different anthropogenic emission inventories for Europe. We applied two regional refinements, i.e. one refinement covering Europe (50 km resolution) and one covering Germany (12 km resolution). The diagnosed absolute contributions of land transport emissions to reactive nitrogen (NOy) near ground level are in the range of 5 to 10 nmol mol−1. This corresponds to relative contributions of 50 % to 70 %. The largest absolute contributions appear around Paris, southern England, Moscow, the Po Valley, and western Germany. The absolute contributions to carbon monoxide range from 30 nmol mol−1 to more than 75 nmol mol−1 near emission hot-spots such as Paris or Moscow. The ozone which is attributed to land transport emissions shows a strong seasonal cycle with absolute contributions of 3 nmol mol−1 during winter and 5 to 10 nmol mol−1 during summer. This corresponds to relative contributions of 8 % to 10 % during winter and up to 16 % during summer. The largest values during summer are confined to the Po Valley, while the contributions in western Europe range from 12 % to 14 %. Only during summer are the ozone contributions slightly influenced by the anthropogenic emission inventory, but these differences are smaller than the range of the seasonal cycle of the contribution to land transport emissions. This cycle is caused by a complex interplay of seasonal cycles of other emissions (e.g. biogenic) and seasonal variations of the ozone regimes. In addition, our results suggest that during events with large ozone values the ozone contributions of land transport and biogenic emissions increase strongly. Here, the contribution of land transport emissions peaks up to 28 %. Hence, our model results suggest that land transport emissions are an important contributor during periods with large ozone values.

Highlights

  • Mobility plays a key role in everyday life, which involves the transport of goods and persons

  • The source attribution of ozone and ozone precursors is performed using the tagging method described in detail by Grewe et al (2017), which is based on an accounting system following the relevant reaction pathways and applies the generalized tagging method introduced by Grewe (2013)

  • During periods of large ozone values, our analyses show that the contribution of land transport emissions to ozone increases strongly, while the contribution of anthropogenic non-traffic emissions is only slightly changed

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Summary

Introduction

Mobility plays a key role in everyday life, which involves the transport of goods and persons. We choose a source attribution method to calculate the contributions of land transport emissions to ozone and ozone precursors. Tagaris et al (2015) quantified the impact of 10 different emission sources on European ozone and PM2.5 levels using the CMAQ (Community Multi-scale Air Quality) model for a specific period (July 2006). Compared to this, Valverde et al (2016) used a source attribution method integrated in CMAQ (Kwok et al, 2015) to investigate the contributions of road traffic emissions of Madrid and Barcelona to ozone. The present study provides a detailed assessment on the contribution of land transport emissions to ozone and ozone precursors (NOx, CO) considering the combined effect of European and global emissions.

Description of the model system
References calculation of aerosol optical properties
Tagging method for source attribution
Emission scenarios and numerical experiments
Model evaluation
Contribution of land transport emissions to ozone in Europe and Germany
Seasonal average contribution to ground-level ozone
Contribution during extreme ozone events
Contribution of land transport emissions to reactive nitrogen in Germany
Contribution of land transport emissions to net ozone production in Europe
Findings
Discussion
Conclusions
Full Text
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