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Volume 43 Issue 11
Nov.  2025
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Article Contents
WANG Bingbing, JI Yaqin, YANG Xiawei, WANG Miao, XIAO Yang, SHI Jingwen, XU Wenju, LIN Zi. Spatial and temporal characteristics of heavy-polluted weather and potential source areas in Beijing-Tianjin-Hebei with the surrounding area in 2021[J]. ENVIRONMENTAL ENGINEERING , 2025, 43(11): 73-83. doi: 10.13205/j.hjgc.202511009
Citation: WANG Bingbing, JI Yaqin, YANG Xiawei, WANG Miao, XIAO Yang, SHI Jingwen, XU Wenju, LIN Zi. Spatial and temporal characteristics of heavy-polluted weather and potential source areas in Beijing-Tianjin-Hebei with the surrounding area in 2021[J]. ENVIRONMENTAL ENGINEERING , 2025, 43(11): 73-83. doi: 10.13205/j.hjgc.202511009

Spatial and temporal characteristics of heavy-polluted weather and potential source areas in Beijing-Tianjin-Hebei with the surrounding area in 2021

doi: 10.13205/j.hjgc.202511009
  • Received Date: 2024-07-01
  • Accepted Date: 2024-08-21
  • Rev Recd Date: 2024-08-02
  • Available Online: 2026-01-09
  • China’s National 14th Five-Year Plan and the 2035 Vision proposes eliminating heavily polluted weather and continuously improving the environmental quality of Beijing-Tianjin-Hebei with the surrounding area (BTHSA). The air pollutant concentration and GDAS data in BTHSA in 2021 were adopted to explore heavy pollution's spatial and temporal characteristics. Then, they were used to analyze the distribution of the airflow trajectories and the primary pollutants’ potential source during the typical heavy pollution processes. The results indicated that: in terms of temporal distribution, BTHSA had no heavy pollution days in August and September, while January and March had the largest day number. Besides, the main primary pollutants were PM2.5, PM10, and O3 during heavy pollution days. Regarding spatial distribution, heavy pollution occurred in the entire region of BTHSA in spring and winter, and only in some areas in summer and autumn. The number of heavily polluted and severely polluted days showed significant spatial aggregation. The analysis of typical heavy pollution processes displayed that: in spring, PM10 in Shijiazhuang was influenced by short-range transport from the east and long-range transport airflow trajectories from the northwest. In summer, O3 in Taiyuan was dominated by emissions from external sources and long-distance transport from the northwest. In autumn, PM2.5 in Hebi was due to local source emissions and short-range transport. In winter, PM2.5 in Kaifeng mainly came from short-range transport from the east. Therefore, countermeasures were proposed including tapping the distribution characteristics and potential source areas of primary pollutants in each heavy pollution process, targeting the development of joint prevention and control measures, and coordinating the prevention and control of air pollution in key regions.
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  • [1]
    ZHU Y Y,WANG W,GAO Y X. Assessment of emission reduction effect in Beijing,Tianjin and surrounding 26 cities from January to March in 2020 during the epidemic of COVID-19[J]. China Environmental Science,2021,41(2):505-516. 朱媛媛,汪巍,高愈霄,等. 疫情期间“2+26”城市污染减排成效评估[J]. 中国环境科学,2021,41(2):505-516.
    [2]
    FENG Y Y,NING M,LEI Y,et al. Defending blue sky in China:Effectiveness of the Air Pollution Prevention and Control Action Plan on air quality improvements from 2013 to 2017[J]. Journal of Environmental Management,2019,252:109603
    [3]
    YANG X,WANG Y,CHEN D,et al. Does the Blue Sky Defense War Policy paint the sky blue?:a case study of Beijing-Tianjin-Hebei Region,China[J]. International Journal of Environmental Research and Public Health,2021,18(23):12397.
    [4]
    WANG Y C,JIANG C L,HE J Y,et al. Emission reduction potential of air pollution from coal burning in the Beijing-Tianjin-Hebei air pollution transmission channel[J]. China Environmental Science,2018,38(7):2401-2405. 王彦超,蒋春来,贺晋瑜,等. 京津冀大气污染传输通道城市燃煤大气污染减排潜力[J]. 中国环境科学,2018,38(7):2401-2405.
    [5]
    HUANG X G,SHAO T J,ZHAO J B,et al. Influencing factors and spatial spillover effects of PM2.5 concentration in Fenwei Plain[J]. China Environmental Science,2019,39(8):3539-3548. 黄小刚,邵天杰,赵景波,等. 汾渭平原PM2.5浓度的影响因素及空间溢出效应[J]. 中国环境科学,2019,39(8):3539-3548.
    [6]
    WU W L,XUE W B,ZHENG Y X,et al. Diurnal regulation of VOCs may not be effective in controlling ozone pollution in China[J]. Atmospheric Environment,2021,256(8):118442.
    [7]
    LIU B X,LI Q,SUN R W. Pollution Characteristics and Factors Influencing the Reduction in Ambient PM2.5 in Beijing from 2018 to 2020[J]. Environmental Science,2023,44(5):2409-2420. 刘保献,李倩,孙瑞雯,等. 2018—2020年北京市大气PM2.5污染特征及改善原因[J]. 环境科学,2023,44(5):2409-2420.
    [8]
    Ministry of Ecology and Environment. China ecological environment status bulletin 2021[R]. Beijing:Ministry of Ecology and Environment,2022. 5. 生态环境部. 2021中国生态环境状况公报[R]. 北京:生态环境部,2022. 5.
    [9]
    LU X,ZHANG S J,XING J,et al. Progress of air pollution control in China and its challenges and opportunities in the ecological civilization era[J]. Engineering,2020,6(12):198-216.
    [10]
    SONG X H,YAN L,LIU W,et al. Spatial and temporal characteristics of PM2.5 and ozone combined pollution in Beijing-Tianjin-Hebei and surrounding areas from 2015 to 2021[J]. Environmental Science,2019,44(4):1841-1851. 宋小涵,燕丽,刘伟,等. 2015—2021年京津冀及周边地区PM2.5和臭氧复合污染时空特征分析[J]. 环境科学,2023,44(4):1841-1851.
    [11]
    CAI W Y,XU X D,CHENG X H,et al. Impact of“blocking” structure in the troposphere on the wintertime persistent heavy air pollution in northern China[J]. Science of the Total Environment,2020. 741:140325
    [12]
    JIN S Y,MA Y F,WANG Q. Analysis of a heavy air pollution process in Shenyang in 2018[J]. Environmental Engineering,2021,39(3):120-129. 金思宇,马云峰,王琦,等. 2018年沈阳市一次空气重污染过程分析[J]. 环境工程,2021,39(3):120-129.
    [13]
    SUN F,YAO H,LIU B X,et al. Characteristics of PM2.5 heavy pollution in Beijing-Tianjin-Hebei and surrounding areas from 2013 to 2019[J]. China Environmental Monitoring,21,37(4):46-53. 孙峰,姚欢,刘保献,等. 2013—2019年京津冀及周边地区PM2.5重污染特征[J]. 中国环境监测,2021,37(4):46-53.
    [14]
    YANG J H,JI Z M,KANG S C,et al. Spatiotemporal variations of air pollutants in western China and their relationship to meteorological factors and emission sources[J]. Environmental Pollution,2019,254:112952.
    [15]
    ZHU Y Y,GAO Y X,WANG W,et al. Evaluation of heavy pollution reduction effect in Beijing-Tianjin-Hebei and surrounding"2+26" cities from October to December 2019[J]. Journal of Environmental Sciences,2018,41(10):4402-4412. 朱媛媛,高愈霄,汪巍,等. 2019年10—12月京津冀及周边“2+26”城市重污染减排效果评估[J]. 环境科学,2020,41(10):4402-4412.
    [16]
    JIANG L,LI S S,YANG W J. Analysis on the characteristics of PM2. 5 in a heavy air pollution episode in Beijing in December 2015[J]. Environmental Engineering,2017,35(9):64-70. 江磊,李珊珊,杨文静,等. 2015年12月北京市一次重污染过程中PM2.5特征分析[J]. 环境工程,2017,35(9):64-70.
    [17]
    SHU L,WANG T,HAN H,et al. Summertime ozone pollution in the Yangtze River Delta of eastern China during 2013—2017:Synoptic impacts and source apportionment[J]. Environmental Pollution,2020,257:113631.
    [18]
    LI Y J,AN X Q,FAN G Z. Transport pathway and potential source area of atmospheric particulates in Beijing[J]. China Environmental Science,2019,39(3):915-927. 李颜君,安兴琴,范广洲. 北京地区大气颗粒物输送路径及潜在源分析[J]. 中国环境科学,2019,39(3):915-927.
    [19]
    ZHAO S. YU Y. QIN D,et al. Analyses of regional pollution and transportation of PM2.5 and ozone in the city clusters of Sichuan Basin,China[J]. Atmospheric Pollution Research,2019,10(2):374-385.
    [20]
    SONG X W,HAO Y P,ZHU X D,et al. Change characteristics,meteorological effects and transport sources of ozone pollution in Linfen City[J]. China Environmental Science,202,42(8):3626-3634. 宋晓伟,郝永佩,朱晓东,等. 临汾市臭氧污染变化特征、气象影响及输送源分析[J]. 中国环境科学,2022,42(8):3626-3634.
    [21]
    XUE W B,FU F,WANG J N,et al. Numerical simulation of PM2.5 transregional transport characteristics in China[J]. China Environmental Sciences,2014,34(6):1361-1368. 薛文博,付飞,王金南,等. 中国PM2.5跨区域传输特征数值模拟研究[J]. 中国环境科学,2014,34(6):1361-1368.
    [22]
    Ministry of Ecology and Environment(MEE). Ambient air quality standard:GB 3095—2012[S]. Beijing:China Standards Press,2012. 生态环境部。环境空气质量标准:GB 3095—2012[S]. 北京:中国标准出版社,2012.
    [23]
    WANG Y Q,ZHANG X Y,DRAXLER R R. TrajStat:GIS-based software that uses various trajectory statistical analysis methods to identify potential sources from long-term air pollution measurement data[J]. Environmental Modelling& Software,2009,24(8):938-939.
    [24]
    KONG X,HE W,QIN N,et al. Comparison of transport pathways and potential sources of PM10,in two cities around a large Chinese lake using the modified trajectory analysis[J]. Atmospheric Research,2013,122(3):284-297.
    [25]
    WANG A P,ZHU B,YIN Y,et al. Aerosol concentration characteristics and potential transport source areas over the top of Huangshan Mountain in summer[J]. China Environmental Science,2014,34(4):852-861. 王爱平,朱彬,银燕,等. 黄山顶夏季气溶胶数浓度特征及其输送潜在源区[J]. 中国环境科学,2014,34(4):852-861.
    [26]
    HU B,LIU T,YANG Y,et al. Characteristics and formation mechanism of surface ozone in a coastal island of Southeast China:influence of sea-land breezes and regional transport[J]. Aerosol and Air Quality Research,2019,19(8):17341748.
    [27]
    ZHAO S,YU Y,QIN D,et al. Analyses of regional pollution and transportation of PM2.5 and ozone in the city clusters of Sichuan Basin,China[J]. Atmospheric Pollution Research,2019,10(2):374-385.
    [28]
    LI X F,ZHANG M J,WANG S J,et al. Change characteristics and influencing factors of air pollution index in China[J]. Environmental Science,2012,33(6):1936-1943. 李小飞,张明军,王圣杰,等. 中国空气污染指数变化特征及影响因素分析[J]. 环境科学,2012,33(6):1936-1943.
    [29]
    LIU X,HUANG H,ZUO J,et al. Effect of summer rainfall on removal of air pollutants[J]. Environmental Pollution and Control,2016,38(3):20-24. 刘星,黄虹,左嘉,等. 夏季降雨对大气污染物的清除影响[J]. 环境污染与防治,2016,38(3):20-24.
    [30]
    WANG S G,WANG J Y,ZHOU Z J,et al. Regional characteristics of three kinds of dust storm events in China[J]. Atmospheric Environment,2005,39(3):509-520.
    [31]
    YU Y,XIA D S,CHEN L H,et al. Change characteristics and causes of PM10 pollution in Lanzhou City[J]. Environmental Science,2010,31(1):22-28. 余晔,夏敦胜,陈雷华,等. 兰州市PM10污染变化特征及其成因分析[J]. 环境科学,2010,31(1):22-28.
    [32]
    WANG X X. Atmospheric chemistry[M]. Beijing:China Meteorological Press,1999. 王明星. 大气化学[M]. 北京:气象出版社. 1999.
    [33]
    HUANG R J,ZHANG Y,BOZZETTI C,et al. High secondary aerosol contribution to particulate pollution during haze events in China[J]. Nature,2014,514(7521),218-222.
    [34]
    WANG W G,LIU M Y,WANG T T,et al. Sulfate formation is dominated by manganese-catalyzed oxidation of SO2 on aerosol surfaces during haze events[J]. Nature Communications,2021,12(1),1993.
    [35]
    ZHANG F J,XU J,MA J Z,et al. Effect of straw burning on inorganic components of PM2.5 in the vicinity of Beijing-Tianjin-Hebei[J]. Journal of Applied Meteorological Science,2019,30(4):467-478. 张方健,徐敬,马建中,等. 京津冀周边秸秆燃烧对PM2.5无机组分影响[J]. 应用气象学报,2019,30(4):467-478.
    [36]
    GUO J E,LI G,LIU X H. Detection of polycyclic aromatic hydrocarbons in atmospheric PM2.5 and its carcinogenic health risk analysis in Taiyuan City in 2018 by high performance liquid chromatography[J]. Preventive Medicine Forum,2012,28(1):23-27. 郭建娥,马利刚,刘旭辉. 2018年太原市大气PM2.5中多环芳烃的高效液相色谱法检测及其致癌健康风险分析[J]. 预防医学论坛,2022,28(1):23-27.
    [37]
    ZHANG Q,ZHAO L Y,GUO Z W. Spatial and temporal distribution characteristics of atmospheric pollutants in Wuhan from 2017 to 2020[J]. Environmental Engineering,2023,41(2):82-90. 张晴,赵丽娅,郭志威,等. 2017—2020年武汉市大气污染物时空分布特征研究[J]. 环境工程,2023,41(2):82-90.
    [38]
    ZHAO S,YIN D,YU Y,et al. PM2.5 and O3 pollution during 2015—2019 over 367 Chinese cities:Spatiotemporal variations,meteorological and topographical impacts[J]. Environment Pollution,2020,264:114694.
    [39]
    XIE J H,LI S,XIAO Z Y. Spatiotemporal variation of total ozone in China over the past 50 years[J]. China Environmental Science,2022,42(7):2977-2987. 谢静晗,李飒,肖钟湧. 50年来中国臭氧总量的时空变化特征研究[J]. 中国环境科学,2022,42(7):2977-2987.
    [40]
    HU A Q,XIE X D,GONG K J,et al. Effects of climate change on summer ozone in China[J]. Environmental Science,2023,44(4):1801-1810. 胡安琪,谢晓栋,龚康佳,等. 气候变化对中国夏季臭氧影响[J]. 环境科学,2023,44(4):1801-1810.
    [41]
    LI L W,XIAO Z M,YANG N,et al. Extinction characteristics and sources of aerosols during heavy pollution process in Tianjin in winter 2020[J]. Journal of Environmental Sciences,2012,42(9):4158-4167. 李立伟,肖致美,杨宁,等. 天津市2020年冬季重污染过程气溶胶消光特性及其来源[J]. 环境科学,2021,42(9):4158-4167.
    [42]
    ZHANG Y,XU J M,WANG Y,et al. Characteristics,meteorological effects and potential source areas of persistent ozone pollution events in Beijing-Tianjin-Hebei region from 2015 to 2020[J]. Chinese Journal of Environmental Sciences,2019,43(6):2714-2721. 张莹,许建敏,汪瑶,等. 京津冀地区2015~2020年臭氧持续污染事件特征、气象影响及潜在源区分析[J]. 中国环境科学,2023,43(6):2714-2721.
    [43]
    WANG G C,WAG J,XIN Y J,et al. Transport routes and potential source areas of PM10 and NO2 in Tianjin[J]. China Environmental Science,2014,34(12):3009-3016. 王郭臣,王珏,信玉洁,等. 天津PM10和NO2输送路径及潜在源区研究[J]. 中国环境科学,2014,34(12):3009-3016.
    [44]
    ZHANG Z D,SHAO T J,HUANG X G. Characteristics and potential sources of PM2.5 pollution in Beijing-Tianjin-Hebei region in 2017[J]. Environmental Engineering,2020,38(2):99-106. 张忠地,邵天杰,黄小刚,等. 2017年京津冀地区PM2.5污染特征及潜在来源分析[J]. 环境工程,2020,38(2):99-106.
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