State Key Laboratory of Atmospheric Boundary Layer Physics and Atmospheric Chemistry, Institute of Atmospheric Physics, Chinese Academy of Sciences, Beijing, 100191, China.
National Research Center for Environmental Analysis and Measurement, Beijing, 100029, China.
Environ Sci Pollut Res Int. 2020 Dec;27(34):42713-42726. doi: 10.1007/s11356-020-10213-4. Epub 2020 Jul 27.
Size-resolved trace metal concentrations at two background sites were assessed during a 1-year observation campaign, with the measurements performed in parallel at two mountain sites, where Mt. Dinghu (DHS) located in the rural region of Pearl River Delta (PRD) and Mt. Gongga (GGS) located in the Tibetan Plateau region. In total, 15 selected trace elements (Mg, Al, K, V, Mn, Fe, Cu, Zn, As, Mo, Ag, Cd, Ba, Tl, and Pb) in aerosol samples were determined using inductively coupled plasma mass spectrometry (ICPMS). The major metals in these two mountain sites were Fe, K, Mg, and Ca with concentrations ranging between 241 and 1452 ng/m, 428 and 1351 ng/m, 334 and 875 ng/m, and 376 and 870 ng/m, respectively, while the trace metals with the lowest concentrations were Mo, Ag, Cd, and Tl with concentrations lower than 4 ng/m in DHS and 2 ng/m in GGS. The pronounced seasonal variability in the trace elements was observed in DHS, with lower concentrations in spring and summer and relatively high in winter and autumn, whereas seasonal variance of trace elements is hardly observed in Mt. Gongga. The size distribution pattern of crustal elements of Al, Mg, K, Ba, and Fe was quite similar in DHS and GGS, which were mainly found in coarse particles peaked at 4.7-5.8 μm. In addition, V, Mo, Ag, and Tl were also concentrated in coarse particles, although the high enrichment factor (EF > 100) of which suggested anthropogenic origin, whereas trace metals of Cd, Mn, Zn, As, Cu, and Pb concentrated in fine mode particles. Specifically, these trace metals peak at approximately 1.5 μm in DHS, while those in GGS peaked at diameter smaller than 0.3 μm, indicating the responsible for long-range transport from the far urban and industrialized areas. Multivariate receptor model combined with the enrichment factor results demonstrated that the trace elemental components at these two background sites were largely contributed from the fossil fuel combustion (55.4% in DHS and 44.0% in GGS) and industrial emissions factors (20.1% vs. 26.5%), which are associated with long distance transport from the coastal area of Southeast China and the Northwestern India, respectively, as suggested by the backward air mass trajectory analysis. Local sources from soil dust contributed a minor variance for trace elements in DHS (9.7%) and GGS (13.8%), respectively.
在为期一年的观测活动中,评估了两个背景地点的按粒径分布的痕量金属浓度,在两个山区地点同时进行测量,其中鼎湖山(DHS)位于珠江三角洲(PRD)的农村地区,而贡嘎山(GGS)位于青藏高原地区。使用电感耦合等离子体质谱法(ICPMS)测定气溶胶样品中 15 种选定的痕量元素(Mg、Al、K、V、Mn、Fe、Cu、Zn、As、Mo、Ag、Cd、Ba、Tl 和 Pb)。这两个山区的主要金属是 Fe、K、Mg 和 Ca,浓度范围分别为 241-1452ng/m、428-1351ng/m、334-875ng/m 和 376-870ng/m,而浓度最低的痕量金属是 Mo、Ag、Cd 和 Tl,浓度均低于 DHS 的 4ng/m 和 GGS 的 2ng/m。在 DHS 中观察到痕量元素的显著季节性变化,春季和夏季浓度较低,冬季和秋季相对较高,而贡嘎山的痕量元素季节性变化则几乎难以观察到。DHS 和 GGS 中的地壳元素 Al、Mg、K、Ba 和 Fe 的粒度分布模式非常相似,它们主要存在于粒径为 4.7-5.8μm 的粗颗粒中。此外,V、Mo、Ag 和 Tl 也集中在粗颗粒中,尽管其高富集因子(EF>100)表明其人为来源,而 Cd、Mn、Zn、As、Cu 和 Pb 等痕量金属则集中在细颗粒中。具体而言,这些痕量金属在 DHS 中约在 1.5μm 处达到峰值,而在 GGS 中则在直径小于 0.3μm 处达到峰值,表明其源自远距离传输,来自遥远的城市和工业化地区。多元受体模型结合富集因子结果表明,这两个背景地点的痕量元素成分主要来自化石燃料燃烧(DHS 为 55.4%,GGS 为 44.0%)和工业排放因子(分别为 20.1%和 26.5%),这与来自中国东南沿海和印度西北部的远距离传输有关,这是通过后向轨迹分析得出的。土壤尘埃的本地源对 DHS(9.7%)和 GGS(13.8%)中的痕量元素变化贡献较小。