Objective classification of pollution weather and typical pollution cases in Sichuan Basin from 2019 to 2021
WANG Cong-cong1, ZHANG Xiao-ling1,2, LU Ning-sheng3
1. Plateau Atmosphere and Environment Key Laboratory of Sichuan Province, College of Atmospheric Sciences, Chengdu University of Information Technology, Chengdu 610225, China; 2. Chengdu Plain Urban Meteorology and Environment Field Scientific Observation and Research Station of Sichuan Province, Chengdu 610225, China; 3. Nanning Meteorological Bureau, Nanning 530029, China
Abstract:In this study, the PCT objective weather classification method was applied to research the sea level pressure field and 700 and 500hPa geopotential height fields in the Sichuan basin from 2019 to 2021, and the relationship between weather conditions and meteorological elements and air pollution was studied with the combination of environmental monitoring data. The results show that:①It is easy to appear PM2.5 pollution during the winter half-year, when the weather type of the sea level is low pressure field, 700hPa for westerly trough type, 500hPa for flat latitudinal type, and the weather elements are characterized by low temperature and high humidity, low boundary layer height, existence of convergence of wind field. ②It is conducive to O3 pollution during the summer half-year, when the sea level weather type is low pressure field, 700hPa with the westerly trough type, 500hPa lying at the back of the westerly trough, controlled by northwest airflow, the meteorology conditions with the characteristics of high temperature, low humidity, high boundary layer height, high radiation intensity and low precipitation. ③The formation of polluted weather is related to the coupling effect of high and low altitude weather patterns. The inverse temperature is a good indicator of pollution during the winter half-year, typical PM2.5 pollution days are accompanied by multi-layer inversion or ground inversion, which limits the vertical diffusion of pollutants. ④The PM2.5 high concentration area is mainly distributed in the west and south of the Sichuan Basin, and the low value areas are found in the northern part of the Sichuan Basin. The spatial distribution of O3 concentration is higher in the Chengdu Plain and the southern part of Sichuan Basin,while the lower concentration in the northeastern part of Sichuan.
王聪聪, 张小玲, 卢宁生. 2019~2021年四川盆地污染天气客观分型及典型污染个例研究[J]. 中国环境科学, 2023, 43(5): 2182-2197.
WANG Cong-cong, ZHANG Xiao-ling, LU Ning-sheng. Objective classification of pollution weather and typical pollution cases in Sichuan Basin from 2019 to 2021. CHINA ENVIRONMENTAL SCIENCECE, 2023, 43(5): 2182-2197.
赵乐陶.四川大气污染治理现状及对策[J].中国国情国力, 2020,(5):74-77. Zhao L T. Current situation and countermeasures of air pollution control in Sichuan Province[J]. China National Situation and National Strength, 2020,(5):74-77.
[2]
李红,鲍捷萌,毕方,等.PM2.5与臭氧污染协同控制:挑战与应对[J].世界环境, 2020,(5):24-29. Li H, Bao J M, Bi F, et al. Collaborative control of PM2.5 and ozone pollution:Challenges and countermeasures[J]. World Environment, 2020,(5):24-29.
[3]
柴发合.我国大气污染治理历程回顾与展望[J].环境与可持续发展, 2020,45(3):5-15. Chai F H. Review and prospect of air pollution treatment in China[J]. Environment and Sustainable Development, 2020,45(3):5-15.
[4]
生态环境部.2021年中国生态环境状况公报(摘录)[J].环境保护, 2022,50(12):61-74. Ministry of Ecology and Environment. Bulletin of China's ecological environment status in 2021(extract)[J]. Environmental Protection, 2022,50(12):61-74.
[5]
Liao T T, Wang S, Ai J, et al. Heavy pollution episodes, transport pathways and potential sources of PM2.5 during the winter of 2013 in Chengdu (China)[J]. Science of the Total Environment, 2017,584/585:1056-1065.
[6]
郭倩,汪嘉杨,周子航,等.成都市一次典型空气重污染过程特征及成因分析[J].环境科学学报, 2018,38(2):629-639. Guo Q, Wang J Y, Zhou Z H, et al. Characteristics and causes of a typical heavy air pollution process in Chengdu[J]. Journal of Environmental Sciences, 2018,38(2):629-639.
[7]
蒋婉婷,谢汶静,王碧菡,等.2014~2016年四川盆地重污染大气环流形势特征分析[J].环境科学学报, 2019,39(1):180-188. Jiang W T, Xie W J, Wang B H, et al. Characteristics of heavy pollution atmospheric circulation over Sichuan Basin from 2014 to 2016[J]. Journal of Environmental Sciences, 2019,39(1):180-188.
[8]
李英杰,陈军辉,韩丽,等.气象因素对成都中心城区近地面臭氧的影响[J].环境科学与技术, 2020,43(S2):7-15. Li Y J, Chen J H, Han L, et al. Influence of meteorological factors on near-surface ozone in Chengdu city[J]. Environmental Science and Technology, 2020,43(S2):7-15.
[9]
Lu X, Zhang L, Chen Y F, et al. Exploring 2016~2017 surface ozone pollution over China Source contributions and meteorological influences[J]. Atmospheric Chemistry and physics, 2019,19(12):8339-8361.
[10]
李源,陆彦彬,白宇,等.基于天津臭氧污染特点的气象条件与天气分型研究[J].中国环境监测, 2022,38(5):56-64. Li Y, Lu Y B, Bai Y, et al. Study on meteorological conditions and weather classification based on characteristics of ozone pollution in Tianjin[J]. China Environmental Monitoring, 2022,38(5):56-64.
[11]
常炉予,许建明,瞿元昊,等.上海市臭氧污染的大气环流客观分型研究[J].环境科学学报, 2019,39(1):169-179. Chang L Y, Xu J M, Qu Y H, et al. Objective classification of atmospheric circulation for ozone pollution in Shanghai[J]. Journal of Environmental Sciences, 2019,39(1):169-179.
[12]
赵娜,马翠平,李洋,等.河北重度污染天气分型及其气象条件特征[J].干旱气象, 2017,35(5):839-846. Zhao N, Ma C P, Li Y, et al. Classification and meteorological conditions of heavy pollution weather in Hebei Province[J]. Journal of Arid Meteorology, 2017,35(5):839-846.
[13]
Liu Y L, Shi G M, Zhan Y, et al. Characteristics of PM2.5 spatial distribution and influencing meteorological conditions in Sichuan Basin, southwestern China[J]. Atmospheric Environment, 2021,253(12):118364.
[14]
Xiang X, Shi G M, Wu X D, et al. The extraordinary trend of the spatial distribution of PM2.5 concentration and its meteorological causes in Sichuan Basin[J]. Atmosphere, 2022,13(6):853.
[15]
Shu L, Wang T J, 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, 2019, 257:113631.
[16]
张莹,王式功,贾旭伟,等.华北地区冬半年空气污染天气客观分型研究[J].环境科学学报, 2018,38(10):3826-3833. Zhang Y, Wang S G, Jia X W, et al. Objective classification of air pollution weather in North China in winter half year[J]. Acta Scientiae Environmental Sinica, 2018,38(10):3826-3833.
[17]
严晓瑜,缑晓辉,杨苑媛,等.银川市臭氧污染天气形势客观分型研究[J].环境科学学报, 2022,42(8):13-25. Yan X Y, Gou X H, Yang Y Y, et al. Objective classification of ozone pollution in Yinchuan[J]. Journal of Environmental Sciences, 2022, 42(8):13-25.
[18]
Zhan C C, Xie M, Fang D X, et al. Synoptic weather patterns and their impacts on regional particle pollution in the city cluster of the Sichuan Basin, China[J]. Atmospheric Environment, 2019,208(JUL.):34-47.
[19]
Ning G C, Yim S, Wang S G, et al. Synergistic effects of synoptic weather patterns and topography on air quality:a case of the Sichuan Basin of China[J]. Climate Dynamics, 2019,53(11):6729-6744.
[20]
杨景朝,赵晓莉,陶勇,等.2016~2019年夏半年成都市区臭氧污染天气特征分析[J].环境科学研究, 2021,34(2):254-262. Yang J C, Zhao X L, Tao Y, et al. Weather characteristics of ozone pollution in Chengdu urban area during the summer half year from 2016 to 2019[J]. Research of Environmental Sciences, 2021,34(2):254-262.
[21]
卢宁生,张小玲,康平,等.成都平原城市群春季臭氧污染天气客观分型与典型过程分析[J].环境科学学报, 2021,41(5):1610-1627. Lu N S, Zhang X L, Kang P, et al. Objective classification and typical process analysis of ozone pollution weather in Chengdu Plain Urban Agglomeration in Spring[J]. Journal of Environmental Sciences, 2021,41(5):1610-1627.
[22]
张莹,王式功,倪长健,等.成都冬季PM2.5污染天气形势的客观分型研究[J].环境科学与技术, 2020,43(5):139-144. Zhang Y, Wang S G, Ni C J, et al. Objective classification of PM2.5 pollution weather in Chengdu in winter[J]. Environmental Science and Technology, 2020,43(5):139-144.
[23]
杜筱筱,杨景朝,赵晓莉,等.成都市秋冬季天气形势客观分型与空气质量关联研究[J].环境科学与管理, 2021,46(1):58-62. Du X X, Yang J C, Zhao X L, et al. Correlation between objective classification of autumn and winter weather patterns and air quality in Chengdu[J]. Environmental Science and Management, 2021,46(1):58-62.
[24]
Huth R, Beck C, Philipp A, et al. Classifications of atmospheric circulation patterns:Recent advances and applications[J]. Annals of the New York Academy of Sciences, 2008,1146(1):105-152.
[25]
Philipp A, Beck C, Huth R, et al. Development and comparison of circulation type classifications using the COST 733 dataset and software[J]. International Journal of Climatology, 2016,36.
[26]
Feng X Y, Wei S M, Wang S G. Temperature inversions in the atmospheric boundary layer and lower troposphere over the Sichuan Basin, China:Climatology and impacts on air pollution[J]. Science of the Total Environment, 2020,726:138579.
[27]
张晗,王式功,辛金元,等.基于地基观测订正的MODIS AOD反演四川盆地PM2.5时空分布特征[J].兰州大学学报(自然科学版), 2019,55(5):610-615. Zhang H, Wang S G, Xin J Y, et al. Spatio-temporal distribution of PM2.5 in Sichuan Basin retrieved by MODIS AOD based on ground-based observation correction[J]. Journal of Lanzhou University (Natural Science), 2019,55(5):610-615.
[28]
刘孟琴,汤家法,刘小青,等.四川省近15年以来PM2.5的时空分布特征及原因分析[J].四川环境, 2017,36(3):74-81. Liu M Q, Tang J F, Liu X Q, et al. Spatial and temporal distribution of PM2.5 in Sichuan Province during the past 15 years[J]. Sichuan Environment, 2017,36(3):74-81.
[29]
何沐全,刘志红,张颖,等.川南城市群大气灰霾时空分布特征及成因分析[J].中国环境科学, 2017,37(2):432-442. He M Q, Liu Z H, Zhang Y, et al. Spatial and temporal distribution characteristics and causes of atmospheric haze in southern Sichuan urban agglomeration[J]. China Environmental Science, 2017,37(2):432-442.
[30]
甄英,何静.川南城市群空气质量变化特征及环流影响分析[J].环境工程技术学报, 2022,12(3):693-700. Zhen Y, He J. Air quality change characteristics and circulation influence analysis in southern Sichuan urban agglomeration[J]. Journal of Environmental Engineering Technology, 2022,12(3):693-700.
[31]
曹佳阳,樊晋,罗彬,等.川南四座城市PM2.5化学组分污染特征及其源解析[J].环境化学, 2021,40(2):559-570. Cao J Y, Fan J, Luo B, et al. Pollution characteristics and source analysis of PM2.5 chemical components in four cities in southern Sichuan[J]. Environmental Chemistry, 2021,40(2):559-570.
[32]
邓中慈,康平,胡成媛,等.四川盆地PM2.5时空分布及影响因子研究[J].环境污染与防治, 2020,42(11):1334-1337. Deng Z C, Kang P, Hu C Y, et al. Spatial and temporal distribution of PM2.5 and its influencing factors in Sichuan Basin[J]. Environmental Pollution and Control, 2020,42(11):1334-1337.
[33]
危诗敏,冯鑫媛,张铮子.四川盆地城市群环境空气质量时空分布特征[J].成都信息工程大学学报, 2021,36(1):110-117. Wei S M, Feng X Y, Zhang Z Z. Spatial and temporal distribution of ambient air quality in urban agglomeration of Sichuan Basin[J]. Journal of Chengdu University of Information Technology, 2021,36(1):110-117.
[34]
史文彬,屈坤,严宇,等.成都市夏季臭氧污染的环流分型与来源分析[J].北京大学学报(自然科学版), 2022,58(3):565-574. Shi W B, Qu K, Yan Y, et al. Circulation patterns and sources of ozone pollution in Chengdu in summer[J]. Acta Scientiae Naturae Universitat Pekinensis, 2022,58(3):565-574.
[35]
周子航,邓也,谭钦文,等.四川省人为源大气污染物排放清单及特征[J].环境科学, 2018,39(12):5344-5358. Zhou Z H, Deng Y, Tan Q W, et al. Emission inventory and characteristics of anthropogenic air pollutants in Sichuan Province[J]. Environmental Science, 2018,39(12):5344-5358.
[36]
程念亮,李云婷,张大伟,等.2014年北京市城区臭氧超标日浓度特征及与气象条件的关系[J].环境科学, 2016,37(6):2041-2051. Cheng N L, Li Y T, Zhang D W, et al. Characteristics of excessive daily ozone concentration in urban areas of Beijing in 2014 and its relationship with meteorological conditions[J]. Environmental Science, 2016,37(6):2041-2051.
[37]
杨显玉,吕雅琼,王禹润,等.天气形势对四川盆地区域性臭氧污染的影响[J].中国环境科学, 2021,41(6):2526-2539. Yang X Y, Lv Y Q, Wang Y R, et al. Influence of weather pattern on regional ozone pollution in Sichuan Basin[J]. China Environmental Science, 2021,41(6):2526-2539.
[38]
李培荣,肖天贵.成都地区秋冬季污染天气形势下PM2.5的扩散与输送[J].中国环境科学, 2020,40(1):63-75. Li P R, Xiao T G. Diffusion and transport of PM2.5 under pollution weather in Autumn and winter in Chengdu Area[J]. China Environmental Science, 2020,40(1):63-75.
[39]
田开文,朱江,王自发,等.2020年上半年"COVID-19"疫情期间气象条件变化对四川盆地城市污染物质量浓度影响初步分析[J].气候与环境研究, 2022,27(2):243-262. Tian K W, Zhu J, Wang Z F, et al. Preliminary analysis on the impact of meteorological conditions change on urban pollutant concentration during COVID-19 outbreak in the first half of 2020 in Sichuan Basin[J]. Climatic and Environmental Research, 2022,27(2):243-262.