Abstract

Abstract. Severe ozone (O3) pollution episodes plague a few regions in eastern China at certain times of the year, e.g., the Yangtze River Delta (YRD). However, the formation mechanisms, including meteorological factors, contributing to these severe pollution events remain elusive. A severe summer smog stretched over the YRD region from 22 to 25 August 2016. This event displayed hourly surface O3 concentrations that exceeded 300 µg m−3 on 25 August in Nanjing, an urban area in the western YRD. The weather pattern during this period was characterized by near-surface prevailing easterly winds and continuous high air temperatures. The formation mechanism responsible for this O3 pollution episode over the YRD region, particularly the extreme values over the western YRD, was investigated using observation data and by running simulations with the Weather Research and Forecasting model with Chemistry (WRF-Chem). The results showed that the extremely high surface O3 concentration in the western YRD area on 25 August was largely due to regional O3 transport in the nocturnal residual layer (RL) and the diurnal change in the atmospheric boundary layer. On 24 August, high O3 levels, with peak values of 220 µg m−3, occurred in the daytime mixing layer over the eastern YRD region. During nighttime from 24 to 25 August, a shallow stable boundary layer formed near the surface which decoupled the RL above it from the surface. Ozone in the decoupled RL remained quite constant, which resulted in an O3-rich “reservoir” forming in this layer. This reservoir persisted due to the absence of O3 consumption from nitrogen oxide (NO) titration or dry deposition during nighttime. The prevailing easterly winds in the lower troposphere governed the regional transport of this O3-rich air mass in the nocturnal RL from the eastern to the western YRD. As the regional O3 transport reached the RL over the western YRD, O3 concentrations in the RL accumulated and rose to 200 µg m−3 over the western Nanjing site during the sunrise hours on 25 August. The development of the daytime convective boundary layer after sunrise resulted in the disappearance of the RL, as the vertical mixing in the convective boundary layer uniformly redistributed O3 from the upper levels via the entrainment of O3-rich RL air down to the O3-poor air at the ground. This net downward transport flux reached up to 35 µg m−3 h−1, and contributed a considerable surface O3 accumulation, resulting in severe daytime O3 pollution during the summer smog event on 25 August in the western YRD region. The mechanism of regional O3 transport through the nocturnal RL revealed in this study has great implications regarding understanding O3 pollution and air quality change.

Highlights

  • Tropospheric ozone (O3) is an important atmospheric component and influences climate change and air quality in different ways

  • By analyzing observational data of gaseous species and meteorological variables during severe summer smog over the Yangtze River Delta (YRD) in eastern China in August 2016, we found noteworthy observational evidence of increasing daytime surface O3 levels

  • Governed by prevailing easterly winds in the lower troposphere, the O3-rich air mass in the nocturnal residual layer (RL) shifted from the eastern to the western YRD with a horizontal transport flux of 541 μg m−2 s−1

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Summary

Introduction

Tropospheric ozone (O3) is an important atmospheric component and influences climate change and air quality in different ways. Coupled with the increases in nitrogen oxide (NOx) and volatile organic compound (VOC) emissions, O3 distribution in the lower troposphere is significantly influenced by winds, air temperature, cloud cover and downward shortwave radiation, which all affect the regional transport and chemical formation of O3 (An et al, 2015; Gao et al, 2016; Xu et al, 2008; Li et al, 2018). The ambient O3 level can be affected by the diurnal variation of the atmospheric BL structure over the YRD, with the nighttime stable BL height dropping to 200 m and the daytime BL height reaching up to about 1200 m (Chang et al, 2016).

Observation sites and data
Summer smog in a heat wave episode over the YRD
A potential role of regional O3 transport
Simulation settings
Modeling validation
O3 “reservoir” in the RL
O3 transport in the RL
Contribution of O3 vertical mixing from the RL
25 Aug 115
Conclusions
Full Text
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