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      Low-level summertime isoprene observed at a forested mountaintop site in southern China: implications for strong regional atmospheric oxidative capacity

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          Abstract

          <p><strong>Abstract.</strong> To investigate the atmospheric oxidative capacity (AOC) in forested high mountain areas adjacent to the photochemistry-active Pearl River Delta (PRD) region in southern China, one-month online observations of isoprene and its oxidation products methyl vinyl ketone (MVK) and methacrolein (MACR) were conducted at a national background station in Nanling Mountains in summer 2016. The results showed that the observed daytime isoprene levels (<span class="inline-formula">377±46</span><span class="thinspace"></span>pptv) were significantly lower in comparison with other forest sites within and outside China, although the sampling site was surrounded with subtropical evergreen broad-leaved trees which are strong isoprene emitters. Also, high daytime (MVK<span class="thinspace"></span><span class="inline-formula">+</span><span class="thinspace"></span>MACR)<span class="thinspace"></span><span class="inline-formula">∕</span><span class="thinspace"></span>isoprene ratios (<span class="inline-formula">1.9±0.5</span>) were observed. Based on the observations, we hypothesized that the lower isoprene levels in the study forest might be attributable to a strong AOC in relation to the elevated regional complex air pollution. In further data analyses, high site-level concentrations of daytime OH (<span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M5" display="inline" overflow="scroll" dspmath="mathml"><mrow><mn mathvariant="normal">7.3</mn><mo>±</mo><mn mathvariant="normal">0.5</mn><mo>×</mo><msup><mn mathvariant="normal">10</mn><mn mathvariant="normal">6</mn></msup></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="72pt" height="14pt" class="svg-formula" dspmath="mathimg" md5hash="4ab567b4f0685721a8163971485d3ef9"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-18-14417-2018-ie00001.svg" width="72pt" height="14pt" src="acp-18-14417-2018-ie00001.png"/></svg:svg></span></span><span class="thinspace"></span>molecules<span class="thinspace"></span>cm<span class="inline-formula"><sup>−3</sup>)</span> and nighttime <span class="inline-formula">NO<sub>3</sub></span> radicals (<span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M8" display="inline" overflow="scroll" dspmath="mathml"><mrow><mn mathvariant="normal">6.0</mn><mo>±</mo><mn mathvariant="normal">0.5</mn><mo>×</mo><msup><mn mathvariant="normal">10</mn><mn mathvariant="normal">8</mn></msup></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="72pt" height="14pt" class="svg-formula" dspmath="mathimg" md5hash="84e4f19f6ef9fb8a310e5d91b89a673b"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-18-14417-2018-ie00002.svg" width="72pt" height="14pt" src="acp-18-14417-2018-ie00002.png"/></svg:svg></span></span><span class="thinspace"></span>molecules<span class="thinspace"></span>cm<span class="inline-formula"><sup>−3</sup>)</span> were estimated by using a photochemical box model incorporating the master chemical mechanism (PBM-MCM), and high regional mixing ratios of OH (<span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M10" display="inline" overflow="scroll" dspmath="mathml"><mrow><mn mathvariant="normal">19.7</mn><mo>±</mo><mn mathvariant="normal">2.3</mn><mo>×</mo><msup><mn mathvariant="normal">10</mn><mn mathvariant="normal">6</mn></msup></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="78pt" height="14pt" class="svg-formula" dspmath="mathimg" md5hash="df4d6b2943fd48a62a518aec8017dbf2"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-18-14417-2018-ie00003.svg" width="78pt" height="14pt" src="acp-18-14417-2018-ie00003.png"/></svg:svg></span></span><span class="thinspace"></span>molecules<span class="thinspace"></span>cm<span class="inline-formula"><sup>−3</sup>)</span> during 09:00–15:00<span class="thinspace"></span>LT were also obtained by applying a parameterization method with measured aromatic hydrocarbons. And besides, high initial mixing ratios (<span class="inline-formula">1213±108</span><span class="thinspace"></span>pptv) and short atmospheric reaction time (0.27<span class="thinspace"></span>h) of isoprene during the day were derived by a sequential reaction approach. All these indicate that isoprene was rapidly and highly oxidized in this forest, which supports our hypothesis. The study suggests that the complex air pollution in the PRD may have significantly elevated the background AOC of the adjacent forests, and probably affects the regional air quality and ecological environment in the long term. The feedback of forest ecosystems to the increasing AOC in southern China warrants further studies.</p>

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            High concentrations of ozone in urban and industrial regions worldwide have long been a major air quality issue. With the rapid increase in fossil fuel consumption in China over the past three decades, the emission of chemical precursors to ozone-nitrogen oxides and volatile organic compounds-has increased sharply, surpassing that of North America and Europe and raising concerns about worsening ozone pollution in China. Historically, research and control have prioritized acid rain, particulate matter, and more recently fine particulate matter (PM2.5). In contrast, less is known about ozone pollution, partly due to a lack of monitoring of atmospheric ozone and its precursors until recently. This review summarizes the main findings from published papers on the characteristics and sources and processes of ozone and ozone precursors in the boundary layer of urban and rural areas of China, including concentration levels, seasonal variation, meteorology conducive to photochemistry and pollution transport, key production and loss processes, ozone dependence on nitrogen oxides and volatile organic compounds, and the effects of ozone on crops and human health. Ozone concentrations exceeding the ambient air quality standard by 100-200% have been observed in China's major urban centers such as Jing-Jin-Ji, the Yangtze River delta, and the Pearl River delta, and limited studies suggest harmful effect of ozone on human health and agricultural corps; key chemical precursors and meteorological conditions conductive to ozone pollution have been investigated, and inter-city/region transport of ozone is significant. Several recommendations are given for future research and policy development on ground-level ozone.
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              The tropospheric degradation of volatile organic compounds: a protocol for mechanism development

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                Author and article information

                Journal
                Atmospheric Chemistry and Physics
                Atmos. Chem. Phys.
                Copernicus GmbH
                1680-7324
                2018
                October 09 2018
                : 18
                : 19
                : 14417-14432
                Article
                10.5194/acp-18-14417-2018
                ed5760d3-51db-426f-bd4d-c5fed4cf301c
                © 2018

                https://creativecommons.org/licenses/by/4.0/

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