Abstract

Abstract. Non-methane volatile organic compounds (NMVOCs) are important ozone and secondary organic aerosol precursors and play important roles in tropospheric chemistry. In this work, we estimated the total and speciated NMVOC emissions from China's anthropogenic sources during 1990–2017 by using a bottom-up emission inventory framework and investigated the main drivers behind the trends. We found that anthropogenic NMVOC emissions in China have been increasing continuously since 1990 due to the dramatic growth in activity rates and absence of effective control measures. We estimated that anthropogenic NMVOC emissions in China increased from 9.76 Tg in 1990 to 28.5 Tg in 2017, mainly driven by the persistent growth from the industry sector and solvent use. Meanwhile, emissions from the residential and transportation sectors declined after 2005, partly offsetting the total emission increase. During 1990–2017, mass-based emissions of alkanes, alkenes, alkynes, aromatics, oxygenated volatile organic compounds (OVOCs) and other species increased by 274 %, 88 %, 4 %, 387 %, 91 % and 231 %, respectively. Following the growth in total NMVOC emissions, the corresponding ozone formation potential (OFP) increased from 38.2 Tg of O3 in 1990 to 99.7 Tg of O3 in 2017. We estimated that aromatics accounted for the largest share (43 %) of the total OFP, followed by alkenes (37 %) and OVOCs (10 %). Growth in China's NMVOC emissions was mainly driven by the transportation sector before 2000, while industry and solvent use dominated the emission growth during 2000–2010. Since 2010, although emissions from the industry sector and solvent use kept growing, strict control measures on transportation and fuel transition in residential stoves have successfully slowed down the increasing trend, especially after the implementation of China's clean air action since 2013. However, compared to large emission decreases in other major air pollutants in China (e.g., SO2, NOx and primary PM) during 2013–2017, the relatively flat trend in NMVOC emissions and OFP revealed the absence of effective control measures, which might have contributed to the increase in ozone during the same period. Given their high contributions to emissions and OFP, tailored control measures for solvent use and industrial sources should be developed, and multi-pollutant control strategies should be designed to mitigate both PM2.5 and ozone pollution simultaneously.

Highlights

  • With rapid economic growth and urbanization, high concentrations of ground ozone and aerosols have caused severe adverse effects on air quality, ecosystems and human health (Monks et al, 2015; Lu et al, 2018)

  • Regarding oxygenated volatile organic compounds (OVOCs), we reviewed the profiles for all combustion-related sources, including the combustion of coal, fuel oil, gasoline and diesel in the power, industry, residential and transportation sectors, and corrected the incomplete profiles that were absent from the OVOC fractions

  • We extended the revision to all combustion processes and corrected their profiles by appending the component of OVOCs with fractions derived from the “complete” profiles for the same source

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Summary

Introduction

With rapid economic growth and urbanization, high concentrations of ground ozone and aerosols have caused severe adverse effects on air quality, ecosystems and human health (Monks et al, 2015; Lu et al, 2018). Previous studies revealed that reducing NMVOC emissions from anthropogenic sources is crucial for controlling ozone and fine particulate matter (PM2.5; with aerodynamic diameters less than or equal to 2.5 μm) pollution in Chinese cities (Shao et al, 2009; Yuan et al, 2013; Jin et al, 2015). Despite considering local statistics and measurements, uncertainties in NMVOC emissions are still high, i.e., ±68 %–±78 %, due to a lack of accurate information for a variety of sources such as solvent use, residential fuel combustion, etc. Dramatic changes in NMVOC emissions have taken place in China that are driven by economic development as well as implementation of control measures for the major sectors of industry, residential use and transportation (Wu et al, 2016; Li et al, 2017; Zheng et al, 2018). China has implemented stringent clean air policies to mitigate emissions in recent years, driving the significant reductions in emissions of air pollutants during 2013–2017 (Zheng et al, 2018)

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