Abstract

Abstract. In this work, the impact of Los Angeles Basin pollution transport and stratospheric intrusions on the surface ozone levels observed in the San Gabriel Mountains is investigated based on a combination of surface and lidar measurements as well as WRF-Chem (Weather Research and Forecasting with Chemistry) and WACCM (Whole Atmosphere Community Climate Model) runs. The number of days with observed surface ozone levels exceeding the National Ambient Air Quality Standards exhibit a clear seasonal pattern, with a maximum during summer, when models suggest a minimum influence of stratospheric intrusions and the largest impact from Los Angeles Basin pollution transport. Additionally, measured and modeled surface ozone and PM10 were analyzed as a function of season, time of the day, and wind direction. Measurements and models are in good qualitative agreement, with maximum surface ozone observed for southwest and west winds. For the prevailing summer wind direction, slightly south of the ozone maximum and corresponding to south-southwest winds, lower ozone levels were observed. Back trajectories suggest that this is associated with transport from the central Los Angeles Basin, where titration limits the amount of surface ozone. A quantitative comparison of the lidar profiles with WRF-Chem and WACCM models revealed good agreement near the surface, with models showing an increasing positive bias as function of altitude, reaching 75 % at 15 km above sea level. Finally, three selected case studies covering the different mechanisms affecting the near-surface ozone concentration over the San Gabriel Mountains, namely stratospheric intrusions and pollution transport, are analyzed based on surface and ozone lidar measurements, as well as co-located ceilometer measurements and models.

Highlights

  • A high concentration of near-surface ozone poses a hazard to human health (WHO, 2003), animals, and vegetation (Mauzerall and Wang, 2001)

  • Consistent efforts regulating the emissions of ozone precursors in the Los Angeles (LA) Basin region have led to a considerable reduction in the near-surface ozone levels (Pollack et al, 2013), the LA Basin is still marked as a non-attainment area (EPA, 2020)

  • Many mountaintop monitoring stations have been typically assumed to sample free-troposphere air and have been used as part of a general effort to investigate long-term trends in background trace gas mixing ratios. While this assumption might be true in some stations or during particular periods, an assessment of the impact of local anthropogenic pollution sources is crucial to determine how well and during which periods this assumption of freetroposphere sampling can be considered accurate (Lee et al, 2015; Tsamalis et al, 2014)

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Summary

Introduction

A high concentration of near-surface ozone poses a hazard to human health (WHO, 2003), animals, and vegetation (Mauzerall and Wang, 2001). Consistent efforts regulating the emissions of ozone precursors in the Los Angeles (LA) Basin region have led to a considerable reduction in the near-surface ozone levels (Pollack et al, 2013), the LA Basin is still marked as a non-attainment area (EPA, 2020) For this reason, there has been an increased interest in understanding and modeling the different processes driving the near-surface ozone concentration with the aim to generate more effective air quality regulation policies (Lin et al, 2017). Many mountaintop monitoring stations have been typically assumed to sample free-troposphere air and have been used as part of a general effort to investigate long-term trends in background trace gas mixing ratios While this assumption might be true in some stations or during particular periods, an assessment of the impact of local anthropogenic pollution sources is crucial to determine how well and during which periods this assumption of freetroposphere sampling can be considered accurate (Lee et al, 2015; Tsamalis et al, 2014).

Site description and data coverage
Vaisala CL51 ceilometer
Surface measurements
ACOM WRF-Chem forecast
ACOM WACCM
General ozone features and model evaluation
Surface ozone and PM10 as function of time and wind direction
Vertical ozone profile
Findings
High-surface-ozone drivers at TMF
Full Text
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