2019
DOI: 10.1039/c9em00098d
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Overview on the spatial–temporal characteristics of the ozone formation regime in China

Abstract: Ozone (O3), a main component in photochemical smog, is a secondary pollutant formed through complex photochemical reactions involving nitrogen oxides (NOx) and volatile organic compounds (VOCs).

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Cited by 103 publications
(60 citation statements)
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References 69 publications
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“…This subsequently increases wintertime precursor oxidation which produces more secondary PM. More discussion of the mechanisms for ozone increase is in Text S6 (He et al, 2017; Jin & Holloway, 2015; Li et al, 2018; Lu et al, 2019; Wang et al, 2017). It is worth noting that recent findings suggest halogen chemistry (not included in our model) could to some extent affect the responses of oxidants to NO x reductions (Li, Badia, et al, 2020; Saiz‐Lopez & von Glasow, 2012; Simpson et al, 2015), but should not change our conclusion regarding the trends of oxidants (see more in Text S7) (Chen et al, 2017, 2018; Fu et al, 2018; Jin & Chu, 2006; Li, Badia, et al, 2020; Liu & Abbatt, 2020; Sarwar et al, 2007; Wang et al, 2016; Wang, Chen, et al, 2019; Wang, Jacob, et al, 2019; Xing et al, 2019; Yarwood et al, 2010).…”
Section: Resultsmentioning
confidence: 99%
“…This subsequently increases wintertime precursor oxidation which produces more secondary PM. More discussion of the mechanisms for ozone increase is in Text S6 (He et al, 2017; Jin & Holloway, 2015; Li et al, 2018; Lu et al, 2019; Wang et al, 2017). It is worth noting that recent findings suggest halogen chemistry (not included in our model) could to some extent affect the responses of oxidants to NO x reductions (Li, Badia, et al, 2020; Saiz‐Lopez & von Glasow, 2012; Simpson et al, 2015), but should not change our conclusion regarding the trends of oxidants (see more in Text S7) (Chen et al, 2017, 2018; Fu et al, 2018; Jin & Chu, 2006; Li, Badia, et al, 2020; Liu & Abbatt, 2020; Sarwar et al, 2007; Wang et al, 2016; Wang, Chen, et al, 2019; Wang, Jacob, et al, 2019; Xing et al, 2019; Yarwood et al, 2010).…”
Section: Resultsmentioning
confidence: 99%
“…China has serious air pollution problems, and fine particulate matter (PM 2.5 ) and ozone (O 3 ) are the two major air pollutants (Lin et al, 2010;Hu et al, 2016;Lu et al, 2019;Wu et al, 2019). The annual average PM 2.5 concentrations were higher than 50 µg m −3 in 26 out of the total 31 provincial capital cities in mainland China during 2013-2014 (Wang et al, 2014a), and the national fourth highest daily maximum 8 h average O 3 (O 3 -8 h) was 86.0 ppb during the warm seasons (April-September) in 2013-2017, which is 6.3 %-30 % higher than that in other industrialized regions of the world (Lu et al, 2018). PM 2.5 alone caused 0.87-1.36 million deaths every year in China, and long-term exposure to O 3 was responsible for an extra 254 000 deaths (Cohen et al, Z. Shi et al: Sensitivity of O 3 and PM 2.5 to meteorology 2017; Silver et al, 2018;Apte et al, 2015;Hu et al, 2017b).…”
Section: Introductionmentioning
confidence: 84%
“…Yin et al (2016) found that the relationship between WS and PM 2.5 has a complicated influence, with higher PM at low and high WS than in light to moderate winds in Beijing from 2008 to 2014. Xu et al (2018) examined the variations of PM 2.5 concentration in January 2017 in China compared to that in January 2016 and found that meteorological conditions of low WS, high humidity, low PBLH, and low PCP contributed to PM 2.5 concentration worsening by 29.7 %, 42.6 %, and 7.9 % in the JJJ region, the Pearl River delta (PRD) region, and the Cheng-Yu Basin (CYB) region, respectively. Ma et al (2019) analyzed the effects of meteorology on air pollution in the Yangtze River delta (YRD) region during 2014-2016 and found that PM 2.5 was highly negatively correlated with WS, while O 3 concentration was positively correlated with T but negatively related to relative humidity.…”
Section: Introductionmentioning
confidence: 99%
“…China has serious air pollution problems and fine particulate matter (PM 2.5 ) and ozone (O 3 ) are the two major air pollutants (Lin et al, 2010;Hu et al, 2016;Lu et al, 2019;Wu et al, 2019). The annual average PM 2.5 concentrations were higher than 50 µg m -3 in 26 out of the total 31 provincial capital cities in mainland China during 2013-2014 (Wang et al, 2014a), and the national 4 th highest daily maximum 8-hour average O 3 (O 3 -8h) is 86.0 ppb during the warm-seasons (April-September) in 2013-2017, which is 6.3-30% higher than that in other industrialized regions of the world (Lu et al, 2018).…”
Section: Introductionmentioning
confidence: 99%