北京市海坨山冬季不同污染过程下气溶胶化学组分及其潜在来源分析

为了探讨京津冀地区冬季背景大气中气溶胶化学组分特征及其来源分布,使用GRIMM 180、单颗粒黑碳光度计（SP2）和高分辨率飞行时间气溶胶质谱仪（HR-TOF-AMS）观测了海坨山2020年12月28日至2021年2月3日PM和化学组分,结合气象数据和HYSPLIT模式,计算了潜在源贡献因子（PSCF）和浓度权重轨迹（CWT）,分析了不同污染过程下PM和气溶胶化学组分的时间演变特征及其潜在来源.结果表明,海坨山冬季沙尘过程主要影响PM₁₀和PM_2.5,对PM₁的影响较小;而霾污染正好相反,主要影响PM₁.化学组分在干净天和霾污染中占PM₁的比例分别为85.0%和73.4%,而在沙尘天仅占PM₁的47.4%.霾污染过程中NO^-₃的质量浓度最大,占PM₁的25.2%;在干净天和沙尘天黑碳（BC）的质量浓度最大,占PM₁的24.1%和12.8%. BC气溶胶的中值直径在干净天...

Variation Characteristics and Potential Sources of the Mt. Haituo Aerosol Chemical Composition in Different Pollution Processes During Winter in Beijing, China

In order to investigate the chemical composition and source apportionment of aerosols during winter in the Beijing-Tianjin-Heibei region, the particular matter (PM) and aerosol chemical composition at Mt. Haituo were observed by using a GRIMM 180, a single-particle soot photometer (SP2), and a high-resolution time-of-flight aerosol mass spectrometer (HR-TOF-AMS) from December 28, 2020 to February 3, 2021. Combining these observations with meteorological data and the HYSPLIT model, we calculated the potential source contribution factor (PSCF) and concentration weighted trajectory (CWT) and analyzed the temporal evolution and potential sources apportionment of PM and aerosol chemical composition under different pollution processes. The results showed that the dust storm process mainly affected PM₁₀ and PM_2.5 in Mt. Haituo during the winter and had a small impact on PM₁; by contrast, haze pollution mainly affected PM₁. Chemical components of aerosol accounted for 85.0% and 73.4% of PM₁ on clean and haze days, respectively, but only 47.4% of PM₁ in dust storm processes. NO₃^- was the chemical component with the largest mass concentration in haze, accounting for 25.2% of PM₁; black carbon (BC) had the largest mass concentration on clean and dust storm days, accounting for 24.1% and 12.8% of PM₁, respectively. The median diameters of BC were 209.7, 207.5, and 204.7 nm on clean, dust storm, and haze days, respectively. D_p/D_c was 2.15 in haze pollution, which was 1.38 and 1.39 times that on dust storm and clean days, respectively. Diurnal variations in PM and aerosol chemical components were different during the different processes. PM₁₀ and PM_2.5had high mass concentrations at night and low mass concentrations during the daytime on clean and dust storm days and had a unimodal distribution with a peak at 14:00 in haze. Diurnal variations in chemical composition had a unimodal distribution on clean days and a bimodal distribution on dust storm and haze days. The chemical compositions of the BC coating layer were different under different processes. The coating layers of BC were mainly NH₄NO₃, (NH₄)₂SO₄, and organic matter on the clean, dust storm, and haze days, respectively. The distribution of potential sources of PM₁ and its chemical components were different under different processes. The high-value area of the potential sources was mainly concentrated in the Beijing-Baoding-Shijiazhuang-Yangquan area in the southwestern portion of the site during dust storms and was mainly concentrated in Yanqing, Huailai, and Changping in the areas around the site during haze.