长江流域资源与环境 >> 2021, Vol. 30 >> Issue (2): 382-396.doi: 10.11870/cjlyzyyhj202102013

• 生态环境 • 上一篇    下一篇

长三角PM 2.5和O 3变化特征及与气象要素的关系

陈优良,李亚倩   

  1. (江西理工大学建筑与测绘工程学院,江西 赣州 341000)
  • 出版日期:2021-02-20 发布日期:2021-03-18

Characteristics of O 3 and PM 2.5 and Its Relationship With Meteorological Factors in Yangtze River Delta

CHEN You-liang, LI Ya-qian   

  1. (School of Architecture and Surveying Engineering, Jiangxi University of Science and Technology, Ganzhou 341000, China)
  • Online:2021-02-20 Published:2021-03-18

摘要: 依据2017年长三角地区的空气质量小时数据,结合同期ECMWF气象资料,采用GIS空间分析、相关性分析和数理统计研究了区域O 3、PM 2.5的时空变化特征及其与气象因素的关系。结果表明:(1)长三角城市群O 3浓度在5和9月值最高,O 3_8 h日变化特征呈拉伸型 S曲线,在19:00、20:00达到浓度峰值,峰值浓度最大的地区是滁州,为111 μg/m 3;O 3空间分布由北到南逐渐降低,并且春季(136.57 μg/m 3)>夏季(117.35 μg/m 3)>秋季(83.23 μg/m 3)>冬季(77.06 μg/m 3);O 3与其前体物CO、NO 2相关性较强;当15<T≤20℃,100<PRS≤100.5 kpa时,O 3浓度超标最严重。(2)PM 2.5浓度月均值呈不规则U型分布,低谷期在7、8月;上海浙江区域日均浓度第一个峰值在9:00~10:00,安徽江苏区域是11:00~12:00,第二个峰值均在21:00;PM 2.5空间分布内陆城市高于沿海城市,冬季(62.21 μg/m 3)>春季(44.70 μg/m 3)≈秋季(44.14 μg/m 3)>夏季(31.33 μg/m 3);与NO 2、SO 2相比,PM 2.5和CO相关性更强;O 3与温度、相对湿度是正相关,与风速、风向、气压、边界层高度、降水量则是负相关,PM 2.5与风向、气压是正相关,与其他因素是负相关;当温度低于5℃,100<PRS≤100.5 kpa时,长三角城市群PM 2.5超标率最高。

Abstract: In recent years, composite pollution caused by particulate pollution and photochemical pollution has become an important pollution problem in large urban agglomerations. Based on the air quality monitoring data of 26 cities in the Yangtze River Delta Urban Agglomeration (YRDUA) in 2017, we analyzed the time series characteristics and pollution status of O 3 and PM 2.5 in the region using mathematical statistics method. Then the grid data of O 3,PM 2.5 was generated by inverse distance weight model to analyze the spatial distribution pattern of O 3 and PM 2.5 in the region. Finally, combined with the meteorological factors of ECMWF in the same period, we discussed the effect of meteorological conditions on the concentration of O 3 and the thresholds for the formation of high O 3 concentration. The results show that: (1) The O 3 concentration in YRDUA is highest in May and September, and the daily variation of O 3_8 h is characterized by a tensile S curve, which reaches the peak concentration at 19:00 and 20:00. The maximum peak concentration is 111 μg/m 3 in Chuzhou; The spatial distribution of O 3 gradually decreased from north to south, and spring(136.57 μg/m 3)> summer(117.35 μg/m 3)> autumn(83.23 μg/m 3)> winter(77.06 μg/m 3); O 3 is significantly correlated with its precursors CO and NO2. When 15<T≤20℃, 100<PRS≤100.5 kpa, O 3 pollution is the most serious. (2) Monthly variation of PM 2.5 concentration is irregularly U-shaped distribution, the trough period is in July and August, the daily variation is double-peak trend, the first peak in Shanghai, Zhejiang region occurs at 9:00 or 10:00, in Anhui, Jiangsu region occurs at 11:00 or 12:00, the second peak is at 21:00; PM 2.5 concentrations higher in inland cities than in coastal cities, Winter(62.21 μg/m3)> Spring(44.70 μg/m3)≈ Autumn(44.14 μg/m3)> Summer (31.33 μg/m3); Compared with NO   and SO2, PM2.5 and CO are more relevant; O3 is positively correlated with temperature and relative humidity, negatively correlated with wind speed, wind direction, air pressure, boundary layer height, and precipitation, PM2.5 is positively correlated with wind direction and air pressure, and negatively correlated with other factors; The temperature is less than 5℃, 100<PRS≤100.5 kpa, PM2.5 exceeding standard rate is highest in YRDUA.

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