Mixing layer transport flux of particulate matter in Beijing, China

被引:31
|
作者
Liu, Yusi [1 ,2 ]
Tang, Guiqian [3 ,4 ]
Zhou, Libo [3 ]
Hu, Bo [3 ]
Liu, Baoxian [5 ,6 ]
Li, Yunting [5 ,6 ]
Liu, Shu [7 ]
Wang, Yuesi [3 ,4 ,8 ]
机构
[1] Chinese Acad Meteorol Sci, China Meteorol Adm, State Key Lab Severe Weather, Beijing 100081, Peoples R China
[2] Chinese Acad Meteorol Sci, China Meteorol Adm, Key Lab Atmospher Chem, Beijing 100081, Peoples R China
[3] Chinese Acad Sci, Inst Atmospher Phys, State Key Lab Atmospher Boundary Layer Phys & Atm, Beijing 100029, Peoples R China
[4] Chinese Acad Sci, Inst Urban Environm, Ctr Excellence Urban Atmospher Environm, Xiamen 361021, Fujian, Peoples R China
[5] Beijing Municipal Environm Monitoring Ctr, Beijing 100048, Peoples R China
[6] Beijing Key Lab Airborne Particulate Matter Monit, Beijing 100048, Peoples R China
[7] Liaoning Ecoenvironm Monitoring Ctr, Shenyang 110031, Liaoning, Peoples R China
[8] Univ Chinese Acad Sci, Beijing 100049, Peoples R China
基金
国家重点研发计划; 中国国家自然科学基金;
关键词
SERIOUS AIR-POLLUTION; REGIONAL TRANSPORT; HEIGHT; QUALITY; IMPACT; PLAIN; URBAN;
D O I
10.5194/acp-19-9531-2019
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Quantifying the transport flux (TF) of atmospheric pollutants plays an important role in understanding the causes of air pollution and in making decisions regarding the prevention and control of regional air pollution. In this study, the mixing layer height (MLH) and wind profile were measured by a ceilometer and Doppler wind radar, respectively, and the characteristics of the atmospheric dilution capability were analyzed using these two datasets. The ventilation coefficient (VC) appears to be the highest in the spring (3940 +/- 2110 m(2) s(-1)) and lower in the summer (2953 +/- 1322 m(2) s(-1)), autumn (2580 +/- 1601 m(2) s(-1)) and winter (2913 +/- 3323 m(2) s(-1)). Combined with the backscatter measured by the ceilometer, vertical profiles of the PM2.5 concentration were obtained and the PM2.5 TF in the mixing layer was calculated. The TF was the highest in the spring at 4.33 +/- 0.69 mg m(-1) s(-1) and lower in the summer, autumn and winter, when the TF values were 2.27 +/- 0.42, 2.39 +/- 0.45 and 2.89 +/- 0.49 mg m(-1) s(-1), respectively. Air pollutants transport mainly occurs between 14:00 and 18:00 LT. The TF was large in the pollution transition period (spring: 5.50 +/- 4.83 mg m(-1) s(-1); summer: 3.94 +/- 2.36 mg m(-1) s(-1); autumn: 3.72 +/- 2.86 mg m(-1) s(-1); winter: 4.45 +/- 4.40 mg m(-1) s(-1)) and decreased during the heavy pollution period (spring: 4.69 +/- 4.84 mg m(-1) s(-1); summer: 3.39 +/- 1.77 mg m(-1) s(-1); autumn: 3.01 +/- 2.40 mg m(-1) s(-1); winter: 3.25 +/- 2.77 mg m(-1) s(-1)). Our results indicate that the influence of the air pollutants transport in the southern regions should receive more focus in the transition period of pollution, while local emissions should receive more focus in the heavy pollution period.
引用
收藏
页码:9531 / 9540
页数:10
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