Abstract

Abstract. Hong Kong, as one of the densely populated metropolises in East Asia, has been suffering from severe photochemical smog in the past decades, though the observed nitrogen oxides (NOx) and total volatile organic compounds (TVOCs) were significantly reduced. This study, based on the observation data in the autumns of 2007, 2013 and 2016, investigated the photochemical ozone (O3) formation and radical chemistry during the three sampling periods in Hong Kong with the aid of a photochemical box model incorporating the Master Chemical Mechanism (PBM–MCM). While the simulated locally produced O3 remained unchanged (p=0.73) from 2007 to 2013, the observed O3 increased (p < 0.05) at a rate of 1.78 ppbv yr−1 driven by the rise in regionally transported O3 (1.77±0.04 ppbv yr−1). Both the observed and locally produced O3 decreased (p < 0.05) from the VOC sampling days in 2013 to those in 2016 at a rate of -5.31±0.07 and -5.52±0.05 ppbv yr−1, respectively. However, a leveling-off (p=0.32) was simulated for the regionally transported O3 during 2013–2016. The mitigation of autumn O3 pollution in this region was further confirmed by the continuous monitoring data, which have never been reported. Benefiting from the air pollution control measures taken in Hong Kong, the local O3 production rate decreased remarkably (p < 0.05) from 2007 to 2016, along with the lowering of the recycling rate of the hydroxyl radical (OH). Specifically, VOCs emitted from the source of liquefied petroleum gas (LPG) usage and gasoline evaporation decreased in this decade at a rate of -2.61±0.03 ppbv yr−1, leading to a reduction of the O3 production rate from 0.51±0.11 ppbv h−1 in 2007 to 0.10±0.02 ppbv h−1 in 2016. In addition, solvent usage made decreasing contributions to both VOCs (rate =-2.29±0.03 ppbv yr−1) and local O3 production rate (1.22±0.17 and 0.14±0.05 ppbv h−1 in 2007 and 2016, respectively) in the same period. All the rates reported here were for the VOC sampling days in the three sampling campaigns. It is noteworthy that meteorological changes also play important roles in the inter-annual variations in the observed O3 and the simulated O3 production rates. Evaluations with more data in longer periods are therefore recommended. The analyses on the decadal changes of the local and regional photochemistry in Hong Kong in this study may be a reference for combating China's nationwide O3 pollution in near future.

Highlights

  • Ground-level ozone (O3) is one of the most representative air pollutants in photochemical smog, produced through photochemical reactions between volatile organic compounds (VOCs) and nitrogen oxides (NOx) in the presence of sunlight (NRC; 1992; Jacob et al, 1999; Guo et al, 2017)

  • We found that the contribution of liquefied petroleum gas (LPG) usage and gasoline evaporation to O3 production significantly decreased (p < 0.05) from the 2007 to 2016 sampling campaign (2007: 0.51±0.11 ppbv h−1; 2013: 0.20±0.03 ppbv h−1; 2016: 0.10±0.02 ppbv h−1), which coincided with the variations in VOCs emitted from LPG

  • With the observation data of O3 and its precursors at a suburban site in Hong Kong, downwind of south China, this study analyzed the inter-annual variations in O3 and its photochemistry, as well as the contributions of VOC sources to the local O3 production rates in 2007, 2013 and 2016

Read more

Summary

Introduction

Ground-level ozone (O3) is one of the most representative air pollutants in photochemical smog, produced through photochemical reactions between volatile organic compounds (VOCs) and nitrogen oxides (NOx) in the presence of sunlight (NRC; 1992; Jacob et al, 1999; Guo et al, 2017). It is well documented that O3 is harmful to human health (Bell et al, 2004), crops (Wang et al, 2005) and natural ecosystems (Ashmore, 2005). The O3 levels in many places are still increasing or not decreasing at the expected rates, in East Asia Wang et al, 2017) The O3 levels in many places are still increasing or not decreasing at the expected rates, in East Asia (Ding et al, 2008; Xu et al, 2008; Parrish et al, 2014; Xue et al, 2014a; Y. Wang et al, 2017)

Objectives
Methods
Results
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call