Abstract

Abstract. The southern Mediterranean region frequently experiences critical levels of photochemical pollutants during summertime. In order to account for the contribution of different atmospheric processes during this type of episodes, the WRF-ARW/HERMES/CMAQ modelling system was applied with high resolution (1 km2, 33 sigma vertical layers, 1 h) to assess the different dynamics in a coastal environment and an inland-continental zone: the North-Eastern and Central Iberian Peninsula (NEIP and CIP, respectively). The former is characterized by a very complex terrain, while the latter behaves as a flat area, which clearly affects the pattern of local flows. A representative type of photochemical pollution episode (occurring over 78% of summer days) which occurred during 17–18 June, 2004 is selected as the study period. The CMAQ Integrated Process Rate provides the hourly contributions of atmospheric processes to net O3, NOx and NMVOCs concentrations. The O3 photochemical formation occurs mainly in downwind areas from the main NOx emission sources during midday. At surface level it accounts for 50 to 75 μg m−3 h−1. The urban areas and main roads, as main sources of NOx emissions, act as O3 sinks, quenching up to −200 μg m−3 per hour during the traffic circulation peaks. The O3 concentration gradient generated, larger during daytime, increases the contribution of diffusion processes to ground-level O3 (up to 200 μg m−3 h−1 fluxes, mainly from upper vertical layers). The maximum positive contributions of gas-phase chemistry to O3 occur in the coastal domain at high levels (around 500 to 1500 m a.g.l.), while in the continental domain they take place in the whole atmospheric column under the PBL. The transport of ozone precursors by advective flows determines the location of the maximum O3 surface concentrations. The O3 chemical formation involves the oxidation of less NMVOCs in the NEIP than in the CIP domains, due to differences in chemical sensitivity between these areas. The dry deposition is an important sink in the lowest layer of the model, together with vertical diffusion flows. Finally, the contributions from cloud processes, wet deposition and heterogeneous chemistry are negligible during the whole episode, characterized by a high solar radiation and neither precipitation nor cloudiness. This process analysis provides new quantitative information about the origin of the peaks of O3 and its precursors, aiding the design of abatement strategies in South-Western Europe.

Highlights

  • Atmospheric chemistry transport model simulations suggest that summertime O3 is enhanced in the entire Mediterranean troposphere, contributing substantially to the radiative forcing of climate and air quality issues (Lawrence et al, 1999; Hauglustaine and Brasseur, 2001; Jimenez et al, 2006)

  • High Elective Resolution Emission Modelling System (HERMES) considers the emissions from the following sources: (1) power generation plants, (2) industrial installations, (3) domestic and commercial fossil fuel use, (4) domestic and commercial solvents use, (5) road transport, (6) ports, (7) airports and (8) biogenic emissions; using a bottom-up approach except for the domestic and commercial fossil fuel use, where a top-down approach was adopted and regional emissions were allocated to fine grid cells by surrogate indexes

  • The surface concentrations of pollutants predicted by the Weather Research and Forecasting (WRF)-ARW/HERMES/CMAQ model are evaluated against hourly data from 45 air quality stations (AQS)

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Summary

Introduction

Atmospheric chemistry transport model simulations suggest that summertime O3 is enhanced in the entire Mediterranean troposphere, contributing substantially to the radiative forcing of climate and air quality issues (Lawrence et al, 1999; Hauglustaine and Brasseur, 2001; Jimenez et al, 2006). The South-Western Europe and the Iberian Peninsula (IP) frequently experience photochemical pollution episodes during summertime, in which O3 and PM10 exceedances of the European air quality targets are registered (EC, 2008). Atmospheric modelling is a fundamental tool to assess the processes contributing to air quality levels in these situations.

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