Center for Excellence in Urban Atmospheric Environment, Institute of Urban Environment, Chinese Academy of Sciences, Xiamen, 361021, PR China; Key Lab of Urban Environment and Health, Institute of Urban Environment, Chinese Academy of Sciences, Xiamen, 361021, PR China; Ningbo Urban Environment Observation and Research Station-NUEORS, Chinese Academy of Sciences, Ningbo, 315800, PR China; State Environmental Protection Key Laboratory of the Cause and Prevention of Urban Air Pollution Complex, Shanghai, 200233, PR China.
Center for Excellence in Urban Atmospheric Environment, Institute of Urban Environment, Chinese Academy of Sciences, Xiamen, 361021, PR China; Key Lab of Urban Environment and Health, Institute of Urban Environment, Chinese Academy of Sciences, Xiamen, 361021, PR China; Ningbo Urban Environment Observation and Research Station-NUEORS, Chinese Academy of Sciences, Ningbo, 315800, PR China.
Environ Pollut. 2016 Nov;218:259-268. doi: 10.1016/j.envpol.2016.06.073. Epub 2016 Jul 16.
Measurement of atmospheric mercury speciation was conducted in a coastal city of the Yangtze River Delta, China from July 2013 to January 2014, in conjunction with air pollutants and meteorological parameters. The mean concentrations of gaseous elemental mercury (GEM), particulate bound mercury (HgP) and reactive gaseous mercury (RGM) were 3.26 ± 1.63 ng m, 659 ± 931 pg m, and 197 ± 246 pg m, respectively. High percentages of HgP during haze days were found, due to the increase in direct emissions and gas-particle partitioning of RGM. The average gas-particle partitioning coefficients (Kp) during moderate or severe haze days (PM2.5 > 150 μg m) were obviously decreased. GEM and HgP were positively correlated with PM2.5, SO, NO and CO, suggesting a significant contribution of anthropogenic sources. Elevated HgP concentrations in cold seasons and in the morning were observed while RGM exhibited different seasonal and diurnal pattern. The ratio of HgP/SO and Pearson correlation analysis suggested that coal combustion was the main cause of increasing atmospheric Hg concentrations. The monitoring site was affected by local, regional and interregional sources. The back trajectory analysis suggested that air mass from northwest China and Huabei Plain contributed to elevated atmospheric Hg in winter and autumn, while southeast China with clean air masses were the major contributor in summer.
本研究于 2013 年 7 月至 2014 年 1 月在长江三角洲的一个沿海城市进行了大气汞形态的测量,同时还监测了空气污染物和气象参数。气态元素汞(GEM)、颗粒结合态汞(HgP)和反应性气态汞(RGM)的平均浓度分别为 3.26±1.63ng/m、659±931pg/m 和 197±246pg/m。霾日时 HgP 的比例较高,这是由于 RGM 的直接排放和气相-颗粒分配增加所致。在中度或重度霾日(PM2.5>150μg/m)时,平均气相-颗粒分配系数(Kp)明显降低。GEM 和 HgP 与 PM2.5、SO、NO 和 CO 呈正相关,表明人为源的贡献显著。在寒冷季节和早晨观察到 HgP 浓度升高,而 RGM 则表现出不同的季节性和日变化模式。HgP/SO 的比值和 Pearson 相关分析表明,煤炭燃烧是大气 Hg 浓度升高的主要原因。监测点受到局地、区域和区域间源的影响。轨迹分析表明,来自中国西北部和华北平原的气团在冬季和秋季导致大气 Hg 升高,而夏季则主要是来自中国东南部的清洁气团。