State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, 18 Shuangqing Road, Beijing, 100085, China.
State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, 18 Shuangqing Road, Beijing, 100085, China; College of Resources and Environment, University of Chinese Academy of Sciences, Beijing, 100049, China.
Environ Res. 2022 Nov;214(Pt 2):113814. doi: 10.1016/j.envres.2022.113814. Epub 2022 Jul 9.
Gaseous elemental Hg (GEM), particulate bound Hg (PBM), and gaseous oxidized Hg (GOM) were monitored at an urban site in Beijing, China during wet seasons (July-November) of 2021. The mean (± standard deviation) GEM, PBM, and GOM concentrations were 3.45 ± 1.27 ng m, 48.2 ± 88.6 pg m, and 13.7 ± 55.0 pg m, respectively. GEM level was stable (generally 3.0-4.0 ng m) and the average concentration was about twice that of the background level in Beijing, while the occasionally very high PBM and GOM concentrations (>1000 pg m) suggest pollution events. Moreover, GEM, CO, and NO exhibit a conspicuous similar diurnal trend with lower values during daytime compared to nighttime under the combined influence of anthropogenic emissions and meteorological factors, and the significantly positive relationship between them indicates that they had similar or common sources. However, the diurnal pattern of reactive Hg (i.e., RM = PBM + GOM) was not pronounced. Both cluster and potential source contribution function analyses show that southern Beijing, Tianjin, as well as central and east Hebei provinces were the dominant source regions for elevated GEM at this monitoring site. The dominant reason for the elevated GEM level (generally >3.5 ng m) during pollution event is that majority of air masses originated from the southern polluted regions of this sampling site and traveled at low heights, while the long-range transport of upper clean air masses and continuous high traveling heights were attributed to the low GEM level (<2.0 ng m) during clean event. Positive matrix factorization results reveal that regional transport of coal fired air pollutants and local vehicle emissions were the dominant contributors to elevated GEM level, while RM mainly originated from local sources.
在中国北京的一个城区站点,于 2021 年雨季(7 月至 11 月)监测了气态元素汞(GEM)、颗粒结合态汞(PBM)和气态氧化态汞(GOM)。GEM、PBM 和 GOM 的平均(±标准偏差)浓度分别为 3.45±1.27ng/m、48.2±88.6pg/m 和 13.7±55.0pg/m。GEM 水平稳定(通常为 3.0-4.0ng/m),平均浓度约为北京背景水平的两倍,而偶尔非常高的 PBM 和 GOM 浓度(>1000pg/m)表明存在污染事件。此外,在人为排放和气象因素的综合影响下,GEM、CO 和 NO 表现出明显相似的日变化趋势,白天浓度低于夜间,它们之间显著的正相关关系表明它们具有相似或共同的来源。然而,反应性汞(即 RM=PBM+GOM)的日变化模式并不明显。聚类和潜在源贡献函数分析均表明,南部北京、天津以及河北中东部是该监测点 GEM 升高的主要源区。污染事件中 GEM 水平升高(通常>3.5ng/m)的主要原因是,大部分气团来自采样点南部污染地区,以低高度移动,而洁净事件中 GEM 水平较低(<2.0ng/m)的主要原因是上清洁空气团的长距离输送和持续的高输送高度。正定矩阵因子分解结果表明,燃煤空气污染物的区域输送和本地车辆排放是 GEM 水平升高的主要贡献者,而 RM 主要来源于本地源。