Characteristics of Ozone Photochemical Reaction and Emission Reduction Strategies in Summer and Autumn in Shangqiu

被引:0
作者
Jiang, Xiao-Mei [1 ]
Sun, Lei-Tao [1 ]
Wang, Ling-Ling [2 ]
Hou, Sheng-Xian [3 ]
Fan, Li-Ya [1 ,4 ,5 ,6 ]
Ye, Dai-Qi [1 ,4 ,5 ,6 ]
机构
[1] School of Environment and Energy, South China University of Technology, Guangzhou
[2] Henan Ecological Environment Monitoring and Safety Center, Zhengzhou
[3] Shangqiu Ecological and Environment Monitoring Center of Henan, Shangqiu
[4] Key Laboratory of Urban Atmospheric Volatile Organic Compounds Pollution Control Technology and Equipment, Guangzhou
[5] Guangdong Provincial Key Laboratory of Atmospheric Environment and Pollution Control, Guangzhou
[6] Guangdong Provincial Engineering and Technology Research Centre for Environment Risk Prevention and Emergency Disposal, Guangzhou
来源
Huanjing Kexue/Environmental Science | 2024年 / 45卷 / 10期
关键词
emission reduction strategy; empirical kinetics(EKMA)curve; ozone(O[!sub]3[!/sub]); photochemical reaction characteristics; relative incremental reaction activity(RIR);
D O I
10.13227/j.hjkx.202310206
中图分类号
学科分类号
摘要
Recently,ozone(O3)pollution in Shangqiu has become increasingly prominent,especially in summer and autumn,crucially affecting the local environmental air quality. Based on the monitoring data of O3 pollution days from the Environmental Monitoring Station in June and September 2022(representing summer and autumn)in Shangqiu,an observation-based model(OBM)was used to study the causes and photochemical reaction characteristics of O3 pollution in the city and precursor emission reduction strategies were studied. The observation results indicated that during summer in Shangqiu,the ρ(O3)and O3 daily maximum 8 h moving concentrations[ρ(MDA8-O3)]were 149.7 μg·m−3 and 195.4 μg·m−3,whereas in autumn,ρ(O3)and ρ(MDA8-O3)were 119.8 μg·m−3 and 173.9 μg·m−3,respectively;the O3 concentration in summer was significantly higher than that in autumn. Ozone sensitivity research showed that the generation of O3 in summer and autumn in Shangqiu was controlled by volatile organic compounds(VOCs). Among them,oxygen-containing volatile organic compounds(OVOCs),aromatic hydrocarbons,and alkenes contributed the most to the ozone generation potential(OFP)and·OH reactivity(L·OH),and the control must have been strengthened. The OBM simulation results indicated that the maximum O3 generation rates in summer and autumn were 23.0×10−9 h−1 and 13.6×10−9 h−1,with maximum net generation rates of 17.4×10−9 h−1 and 10.4×10−9 h−1 and the maximum and maximum net generation rates of O3 in summer were 1.68 times higher than those in autumn,indicating that the photochemical reactions in summer were significantly stronger than those in autumn. Compared with that in summer,the generation of O3 in autumn was greatly influenced by regional inputs from other regions or cities,with a maximum input of 14.2×10−9 h−1. The prevention and control of O3 pollution in the summer and autumn seasons in Shangqiu should mainly focus on controlling VOCs. The reduction ratio of VOCs/nitrogen oxides(NOx)in autumn should be greater than that in summer and the reduction ratios of 3∶1 in summer and 4∶1 in autumn could be adopted for control. © 2024 Science Press. All rights reserved.
引用
收藏
页码:5706 / 5714
页数:8
相关论文
共 45 条
[1]  
Wu Z J, Wang Z L,, Zhang Q,, Et al., Strategical research on refined regulations for regional air quality with climate synergy [J], Strategic Study of CAE, 24, 6, pp. 164-172, (2022)
[2]  
Xiao X, Xu Y Y,, Zhang X R,, Et al., Amplified upward trend of the joint occurrences of heat and ozone extremes in China over 2013-20 [J], Bulletin of the American Meteorological Society, 103, 5, pp. E1330-E1342, (2022)
[3]  
Luo L T, Zhang Y L, Lin Y Q,, Et al., Analysis of photochemical characteristics and sensitivity of atmospheric ozone in Nanjing in summer [J], Environmental Science, 45, 3, pp. 1382-1391, (2024)
[4]  
Lin X,, Trainer M, Liu S C., On the nonlinearity of the tropospheric ozone production [J], Journal of Geophysical Research:Atmospheres, 93, D12, pp. 15879-15888, (1988)
[5]  
Li T N, Qiu J X, Fang C S., A brief analysis of the hazards of ozone in the environment and relevant prevention and treatment[J], World Environment, 5, pp. 16-18, (2020)
[6]  
Liu X,, Gai Y J, Qian W T., Formation mechanism and hazards of near-surface ozone and relevant prevention and control countermeasures[J], World Environment, 5, pp. 36-39, (2020)
[7]  
(2019)
[8]  
Zhang Y, Xu J M, Wang Y,, Et al., Characteristics,meteorological impacts and potential sources of persistent ozone pollution events in Beijing-Tianjin-Hebei Region during 2015~2020 [J], China Environmental Science, 43, 6, pp. 2714-2721, (2023)
[9]  
Wu Y Z,, Zhang X,, Gu J,, Et al., Ozone pollution in Suzhou during the early summertime: formation mechanism and interannual variation[J], Environmental Science, 45, 3, pp. 1392-1401, (2024)
[10]  
Wang M,, Chen W T,, Zhang L,, Et al., Ozone pollution characteristics and sensitivity analysis using an observation-based model in Nanjing,Yangtze River Delta Region of China[J], Journal of Environmental Sciences, 93, pp. 13-22, (2020)