School of Environmental and Chemical Engineering, Shanghai University, Shanghai 200444, China.
Institute of Desert Meteorology, China Meteorological Administration, Urumqi 83002, China.
J Environ Sci (China). 2020 Sep;95:49-57. doi: 10.1016/j.jes.2020.03.043. Epub 2020 Apr 29.
Mass level of fine particles (PM) in main cities in China has decreased significantly in recent years due to implementation of Chinese Clean Air Action Plan since 2013, however, O pollution is getting worse than before, especially in megacities such as in Shanghai. In this work, O and PM were continuously monitored from May 27, 2018 to March 31, 2019. Our data showed that the annual average concentration of PM and O (O-8 hr, maximum 8-hour moving average of ozone days) was 39.35 ± 35.74 and 86.49 ± 41.65 µg/m, respectively. The concentrations of PM showed clear seasonal trends, with higher concentrations in winter (83.36 ± 18.66 µg/m) and lower concentrations in summer (19.85 ± 7.23 µg/m), however, the seasonal trends of O were different with 103.75 ± 41.77 µg/m in summer and 58.59 ± 21.40 µg/m in winter. Air mass backward trajectory, analyzing results of potential source contribution function model and concentration weighted trajectory model implied that pollutants from northwestern China contributed significantly to the mass concentration of Shanghai PM, while pollutants from areas of eastern coastal provinces and South China Sea contributed significantly to the mass level of ozone in Shanghai atmosphere. Mass concentration of twenty-one elements in the PM were investigated, and their relationships with O were analyzed. Mass level of ozone had good correlation with that of Ba (r = 0.64, p < 0.05) and V (r = 0.30, p > 0.05), suggesting vehicle emission pollutants contribute to the increasing concentration of ozone in Shanghai atmosphere.
近年来,由于 2013 年以来中国实施了清洁空气行动计划,中国主要城市的细颗粒物(PM)质量水平显著下降,但 O 污染却比以前更严重,尤其是在上海等特大城市。在这项工作中,我们从 2018 年 5 月 27 日至 2019 年 3 月 31 日连续监测了 O 和 PM。我们的数据显示,PM 和 O(O-8hr,臭氧日最大 8 小时移动平均值)的年平均浓度分别为 39.35±35.74μg/m 和 86.49±41.65μg/m。PM 的浓度表现出明显的季节性趋势,冬季浓度较高(83.36±18.66μg/m),夏季浓度较低(19.85±7.23μg/m),而 O 的季节性趋势则不同,夏季浓度为 103.75±41.77μg/m,冬季浓度为 58.59±21.40μg/m。空气团后向轨迹、潜在源贡献函数模型分析结果和浓度加权轨迹模型表明,来自中国西北地区的污染物对上海 PM 的质量浓度有显著贡献,而来自东部沿海省份和南海地区的污染物对上海大气中臭氧的质量水平有显著贡献。我们研究了 PM 中二十一种元素的质量浓度,并分析了它们与 O 的关系。臭氧质量浓度与 Ba(r=0.64,p<0.05)和 V(r=0.30,p>0.05)有很好的相关性,表明车辆排放污染物对上海大气中臭氧浓度的增加有贡献。