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首页> 外文期刊>Atmospheric Chemistry and Physics Discussions >Worsening urban ozone pollution in China from 2013 to 2017 – Part?1: The complex and varying roles of meteorology
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Worsening urban ozone pollution in China from 2013 to 2017 – Part?1: The complex and varying roles of meteorology

机译:2013年至2017年中国城市臭氧污染恶化 - 部分?1:气象学的复杂和不同的角色

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China has suffered from increasing levels of ozone pollution in urban areas despite the implementation of various stringent emission reduction measures since 2013. In this study, we conducted numerical experiments with an up-to-date regional chemical transport model to assess the contribution of the changes in meteorological conditions and anthropogenic emissions to the summer ozone level from 2013 to 2017 in various regions of China. The model can faithfully reproduce the observed meteorological parameters and air pollutant concentrations and capture the increasing trend in the surface maximum daily 8h average (MDA8) ozone (O3) from 2013 to 2017. The emission-control measures implemented by the government induced a decrease in MDA8 O3 levels in rural areas but an increase in urban areas. The meteorological influence on the ozone trend varied by region and by year and could be comparable to or even more significant than the impact of changes in anthropogenic emissions. Meteorological conditions can modulate the ozone concentration via direct (e.g., increasing reaction rates at higher temperatures) and indirect (e.g., increasing biogenic emissions at higher temperatures) effects. As an essential source of volatile organic compounds that contributes to ozone formation, the variation in biogenic emissions during summer varied across regions and was mainly affected by temperature. China's midlatitude areas (25 to 40°N) experienced a significant decrease in MDA8 O3 due to a decline in biogenic emissions, especially for the Yangtze River Delta and Sichuan Basin regions in 2014 and 2015. In contrast, in northern (north of 40°N) and southern (south of 25°N) China, higher temperatures after 2013 led to an increase in MDA8 O3 via an increase in biogenic emissions. We also assessed the individual effects of changes in temperature, specific humidity, wind field, planetary boundary layer height, clouds, and precipitation on ozone levels from 2013 to 2017. The results show that the wind field change made a significant contribution to the increase in surface ozone over many parts of China. The long-range transport of ozone and its precursors from outside the modeling domain also contributed to the increase in MDA8 O3 in China, especially on the Qinghai–Tibetan Plateau (an increase of 1 to 4ppbv). Our study represents the most comprehensive and up-to-date analysis of the impact of changes in meteorology on ozone across China and highlights the importance of considering meteorological variations when assessing the effectiveness of emission control on changes in the ozone levels in recent years.
机译:尽管自2013年以来,中国遭受了城市地区臭氧污染水平的增加。在本研究中,我们对最新区域化学传输模型进行了数值实验,以评估变化的贡献2013年至2017年夏季臭氧水平的气象条件和人为排放。该模型可以忠实地再现观察到的气象参数和空气污染物浓度,并从2013年到2017年从2013年到2017年捕获表面最大每日8小时(MDA8)臭氧(O3)的增加趋势。政府实施的排放控制措施造成减少农村地区MDA8 O3水平,但城市地区的增加。对臭氧趋势的气象影响因地区和年份而变化,并且可能与人为排放变化的影响相当或更重要。气象条件可以通过直接(例如,在较高温度下增加反应速率)和间接(例如,在较高温度下增加生物发射)的影响来调节臭氧浓度。作为有助于臭氧地层的挥发性有机化合物的必要源,夏季在夏季变化的生物发射变异,主要受温度影响。中国的中美地区(25至40°N)由于生物排放的下降,特别是对于2014年和2015年的长江三角洲和四川盆地地区,在MDA8 O3中经历了显着降低。相比之下,北部(北北n)和南方(25°N南部)中国,2013年后的较高温度导致MDA8 O3的增加通过生物发射增加。我们还评估了2013年至2013年臭氧水平的温度,特定湿度,风场,行星边界层高度,云和降水的个体影响。结果表明,风田改变对增加的贡献产生了重大贡献在中国许多地区的表面臭氧。臭氧的远程运输及其前体来自建模结构域的外部也有助于中国MDA8 O3的增加,特别是在青藏高原(增加1至4ppbv)上。我们的研究代表了对中国臭氧变化影响的最全面,最新分析,并突出了考虑评估排放控制近年来臭氧水平变化的有效性时考虑气象变异的重要性。

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