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2016年10~11月期间北京市大气颗粒物污染特征与传输规律
摘要点击 2972  全文点击 951  投稿时间:2018-10-29  修订日期:2018-11-28
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中文关键词  气溶胶化学组分在线监测仪(ACSM)  非难熔性PM1(NR-PM1)  化学组分  潜在源贡献分析(PSCF)法  气象-空气质量模式(WRF-CAMx)  PM2.5传输通量
英文关键词  Aerosol Chemical Speciation Monitor (ACSM)  non-refractory submicron aerosols (NR-PM1)  chemical components  potential source contribution function (PSCF) method  meteorology-air quality coupling model system (WRF-CAMx)  PM2.5 transport flux
作者单位E-mail
张晗宇 北京工业大学环境与能源工程学院, 区域大气复合污染防治北京市重点实验室, 北京 100124 zhy2016@emails.bjut.edu.cn 
程水源 北京工业大学环境与能源工程学院, 区域大气复合污染防治北京市重点实验室, 北京 100124 bjutpaper@gmail.com 
姚森 北京工业大学环境与能源工程学院, 区域大气复合污染防治北京市重点实验室, 北京 100124  
王晓琦 北京工业大学环境与能源工程学院, 区域大气复合污染防治北京市重点实验室, 北京 100124  
张俊峰 北京工业大学环境与能源工程学院, 区域大气复合污染防治北京市重点实验室, 北京 100124  
中文摘要
      本研究采用气溶胶化学组分在线监测仪(ACSM)对北京地区2016年10月15日~11月15日期间非难熔性PM1(NR-PM1)化学组分进行实时连续在线观测,探讨了NR-PM1化学组分的演变特征;运用潜在源贡献分析(PSCF)法和气象-空气质量模式(WRF-CAMx)识别了北京PM2.5潜在污染源区和传输路径,揭示了PM2.5净传输通量的垂直分布特征.结果表明,北京秋季NR-PM1和PM2.5质量浓度分别为(59.16±57.05)μg·m-3和(89.82±66.66)μg·m-3,其中NR-PM1平均占PM2.5的(70.31±22.28)%.整个观测期间,有机物(Org)、硝酸盐(NO3-)、硫酸盐(SO42-)、铵盐(NH4+)和氯化物(Chl)分别占NR-PM1总质量浓度的(42.75±11.35)%、(21.27±7.72)%、(19.11±7.08)%、(12.19±2.64)%和(4.68±3.24)%,不同化学组分的日变化特征存在明显差异.对北京秋季NR-PM1污染影响较大的潜在源区主要集中在河北南部、河南东北部及山东西部,重污染期间保定、北京南部及廊坊等城市对NR-PM1贡献较大.WRF-CAMx模拟结果表明,PM2.5总的净传输通量呈现出显著的垂直分布特征.整个观测期间,毗邻城市主要向北京输入PM2.5,净通量最大出现在海拔600~1000 m;而重污染前期外来源输送PM2.5主要位于高空,直到污染最严重的11月5日,PM2.5转为近地面传输,说明高空和近地面传输是影响北京秋季PM2.5重污染形成的重要因素.同时鉴别出了两种传输路径,即西南-东北方向(保定→北京→承德)和西北-东南方向(张家口→北京→廊坊北→天津).
英文摘要
      In this study, the Aerosol Chemical Speciation Monitor (ACSM) was used to conduct real-time and continuous comprehensive observation of chemical components in non-refractory submicron aerosols (NR-PM1) from October 15 to November 15, 2016. In addition to that, the evolution characteristics of NR-PM1 chemical components were discussed. The potential source contribution function (PSCF) method and a meteorology-air quality coupling model system (WRF-CAMx) were applied to identify the potential PM2.5 emission sources and transport path in Beijing, and the vertical distribution characteristics of PM2.5 net transport flux. The results indicate that the monthly average mass concentrations of NR-PM1 and PM2.5 were (59.16±57.05) μg·m-3 and (89.82±66.66) μg·m-3, respectively. On average, NR-PM1 accounted for (70.31±22.28)% of PM2.5. During the whole study period, Org, NO3-, SO42-, NH4+, and Chl represented (42.75±11.35)%, (21.27±7.72)%, (19.11±7.08)%, (12.19±2.64)%, and (4.68±3.24)% of NR-PM1, respectively. The diurnal variation characteristics of different chemical components were disparate. The high potential source areas were mainly located in southern Hebei, northeastern Henan, and western Shandong provinces during the whole study period. During the haze episode, the potential regions of higher contribution were concentrated in Baoding, southern Beijing, and Langfang. The simulation results of WRF-CAMx showed that the vertical distribution characteristics of PM2.5 net flux varied with different altitudes. The adjacent cities mainly export PM2.5 to Beijing, and the PM2.5 net fluxes mainly occurred at 600-800 m during the whole study period. PM2.5 in Beijing from external sources mainly occurred in high altitudes during the early stage of the heavy pollution episode. Then it turned to near-ground transport until November 5, when the pollution was the most severe. This indicated that high-altitude and near-ground transport both played an essential role in the formation of heavy PM2.5 pollution in Beijing during the autumn. Moreover, two important transport pathways were identified:the southwest-northeast pathway (Baoding→Beijing→Chengde) and the northwest-southeast pathway (Zhangjiakou→Beijing→Langfang-south→Tianjin).

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