2021
DOI: 10.1016/j.atmosenv.2020.118130
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Rising surface ozone in China from 2013 to 2017: A response to the recent atmospheric warming or pollutant controls?

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Cited by 43 publications
(19 citation statements)
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“…Zhao et al, 2013). Since the enactment of the Air Pollution Prevention and Control Action Plan in 2013, the Chinese government has taken drastic measures to reduce the emissions of sulfur dioxide (SO 2 ), nitrogen oxides (NO x ) and primary PM 2.5 , leading to significant decreases in sulfate and overall PM 2.5 concentrations in cities (Silver et al, 2018;Li et al, 2021a;. Meanwhile, the nitrogen / sulfur (N/S) ratio in PM 2.5 increased significantly, and nitrate became the main component of PM 2.5 (16 %-45 %) during haze episodes, despite a more than 20 % reduction in the concentrations of its precursor NO x (Shao et al, 2018;Wen et al, 2018;Zhai et al, 2019).…”
Section: Introductionmentioning
confidence: 99%
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“…Zhao et al, 2013). Since the enactment of the Air Pollution Prevention and Control Action Plan in 2013, the Chinese government has taken drastic measures to reduce the emissions of sulfur dioxide (SO 2 ), nitrogen oxides (NO x ) and primary PM 2.5 , leading to significant decreases in sulfate and overall PM 2.5 concentrations in cities (Silver et al, 2018;Li et al, 2021a;. Meanwhile, the nitrogen / sulfur (N/S) ratio in PM 2.5 increased significantly, and nitrate became the main component of PM 2.5 (16 %-45 %) during haze episodes, despite a more than 20 % reduction in the concentrations of its precursor NO x (Shao et al, 2018;Wen et al, 2018;Zhai et al, 2019).…”
Section: Introductionmentioning
confidence: 99%
“…A confounding factor is that, for most cities in China, the production of O 3 is usually limited by VOCs (Xie et al, 2014;Dong et al, 2014;Liu et al, 2010). The control of NO x emissions has therefore resulted in an increase of surface O 3 concentrations in recent years (Li et al, 2021a;Kalsoom et al, 2021), implying complex impacts on nitrate formation. Li et al (2021a) and examined the influencing factors on the surface O 3 trends in China from 2013 to 2017 using regional chemical models.…”
Section: Introductionmentioning
confidence: 99%
“…The model statistical evaluations show a MB of −3.66, −1.14, 4.7 and 18.32 μg m −3 , and NMB of −9.92, −6.46, 16.47 and 7.72% for PM2.5, SO2, NO2 and O3 in Period I, and a relatively larger MB of −27.31, −11.65, 1.27 and −39.01 μg m −3 , and NMB of −29.82, −28.11, 2.40 and −31.05% in Period II, respectively (Table 3). The uncertainty in emissions data, the absence of secondary organic aerosol in MOSAIC aerosol chemistry or the simulated wind errors may be responsible for the larger atmospheric chemical biases in winter, which has been extensively discussed in some studies (Zhao et al, 2016;Li et al, 2021a).…”
Section: Model Weather and Chemical Validationmentioning
confidence: 99%
“…Secondary inorganic aerosols (SIA), including sulfate (SO4 2-), nitrate (NO3 -) and ammonium (NH4 + ) account for 30-60% of the total fine particulate matter (PM2.5) mass during haze events in China (Huang et al, 2014a;Zhao et al, 2013). Since the enactment of the Air Pollution Action Plan in 2013, the Chinese government has taken drastic measures to reduce the emissions of sulfur dioxide (SO2), nitrogen oxides (NOx) and primary PM2.5, leading to significant decreases in sulfate and overall PM2.5 concentrations in cities (Silver et al, 2018;Li et al, 2021a;Wang et al, 2017). Meanwhile, the nitrogen/sulfur (N/S) ratio in PM2.5 increased significantly and nitrate had been the main component of PM2.5 (16-45%) during haze episodes, despite a more than 20% reduction in the concentrations of its precursor NOx (Shao et al, 2018;Wen et al, 2018;Zhai et al, 2019).…”
Section: Introductionmentioning
confidence: 99%
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