临汾市臭氧时空变化特征及影响因素分析
Characteristics of Spatial and Temporal Variations of Ozone in Linfen City and Analysis of Influencing Factors
DOI: 10.12677/ag.2024.146069, PDF,    科研立项经费支持
作者: 宋 朕:河北工程大学地球科学与工程学院,河北 邯郸;中国环境科学研究院环境基准与风险评估国家重点实验室,北京;营 娜, 薛志钢:中国环境科学研究院环境基准与风险评估国家重点实验室,北京;宋宏利*:河北工程大学地球科学与工程学院,河北 邯郸
关键词: O3时空变化特征影响因素O3 Characteristics of Spatial and Temporal Variations Influencing Factors
摘要: 近年来,我国城市环境空气中PM2.5浓度逐年下降,O3浓度日趋升高,O3污染已成为制约空气质量改善的关键因素。临汾市作为中国重要焦煤基地之一,拥有大量的钢铁、焦化等行业,这些行业排放的污染物,导致O3浓度居高不下,污染治理面临着严峻挑战。本研究基于2020~2022年临汾市监测站点的污染物浓度及气象数据,采用因果性分析、复杂网络及相关性分析方法解析临汾市O3浓度的时空变化特征和影响因素。2020~2022年临汾市O3污染较为严重,从时间上看,O3污染期为5~9月,非污染期为10~2月。从空间上看,临汾市各站O3日最大8小时滑动均值均超过160 μg/m3,O3污染期内的O3浓度传输网络模型连边值均超过0.5,说明各站点间存在显著的O3传输关系,其中市委和城南的O3污染最为明显,传输能力最强。从影响因素上看,O3与NO2负相关关系显著,与PM2.5、CO、PM10、SO2负相关关系较弱。同时,O3与气压、相对湿度呈负相关,而与气温、露点温度、十分钟平均风速和能见度呈正相关。
Abstract: In recent years, the concentration of PM2.5 in China’s urban ambient air has been decreasing year by year, and the concentration of O3 has been increasing, and O3 pollution has become a key factor restricting the improvement of air quality. Linfen city, as one of the important coking coal bases in China, has a large number of iron and steel and coking industries, which emit pollutants, resulting in high O3 concentrations and facing serious challenges in pollution management. Based on the pollutant concentrations and meteorological data from the monitoring stations in Linfen City from 2020 to 2022, this study uses causality analysis, complex network and correlation analysis to analyse the spatial and temporal characteristics of the O3 concentration and the influencing factors in Linfen City. In 2020~2022, Linfen City is more seriously polluted by O3, and from the time point of view, the O3 polluted period is from May to September, and the non-polluted period is from October to February. From the spatial point of view, the daily maximum 8-hourly sliding mean values of O3 at each station in Linfen City exceeded 160 μg/m3, and the contiguous edge values of the O3 concentration transport network model during the O3 pollution period exceeded 0.5, which indicated that there was a significant O3 transport relationship between stations, with the Municipal Party Committee and the southern part of the city being the most obvious O3 pollutants with the strongest transport capacity. In terms of influencing factors, O3 has a significant negative correlation with NO2, and a weaker negative correlation with PM2.5, CO, PM10, and SO2. Meanwhile, O3 was negatively correlated with barometric pressure and relative humidity, while positively correlated with air temperature, dew point temperature, ten-minute average wind speed and visibility.
文章引用:宋朕, 营娜, 薛志钢, 宋宏利. 临汾市臭氧时空变化特征及影响因素分析[J]. 地球科学前沿, 2024, 14(6): 743-752. https://doi.org/10.12677/ag.2024.146069

参考文献

[1] Murray, C.J.L., Aravkin, A.Y., Zheng, P., Abbafati, C., Abbas, K.M., Abbasi-Kangevari, M., et al. (2020) Global Burden of 87 Risk Factors in 204 Countries and Territories, 1990-2019: A Systematic Analysis for the Global Burden of Disease Study 2019. The Lancet, 396, 1223-1249. [Google Scholar] [CrossRef] [PubMed]
[2] Bowdalo, D., Petetin, H., Jorba, O., Guevara, M., Soret, A., Bojovic, D., et al. (2022) Compliance with 2021 WHO Air Quality Guidelines across Europe Will Require Radical Measures. Environmental Research Letters, 17, Article ID: 021002. [Google Scholar] [CrossRef
[3] Martins, N.R. and Carrilho da Graça, G. (2018) Impact of PM2.5 in Indoor Urban Environments: A Review. Sustainable Cities and Society, 42, 259-275. [Google Scholar] [CrossRef
[4] 佚名. 2021年中国生态环境状况公报(摘录) [J]. 环境保护, 2022, 50(12): 61-74.
[5] 张晓娟. 基于Stacking模型的北京市近地面臭氧浓度预测[D]: [硕士学位论文]. 太原: 山西大学, 2023.[CrossRef
[6] Wei, J., Li, Z., Xue, W., Sun, L., Fan, T., Liu, L., et al. (2021) The Chinahighpm10 Dataset: Generation, Validation, and Spatiotemporal Variations from 2015 to 2019 across China. Environment International, 146, Article ID: 106290. [Google Scholar] [CrossRef] [PubMed]
[7] 北京大学统计科学中心环境统计组. 空气质量评估报告(十): “3 + 110”城市2013-2022年区域污染状况评估[R]. 北京: 北京大学, 2023.
[8] Orellano, P., Reynoso, J., Quaranta, N., Bardach, A. and Ciapponi, A. (2020) Short-Term Exposure to Particulate Matter (PM10 and PM2.5), Nitrogen Dioxide (NO2), and Ozone (O3) and All-Cause and Cause-Specific Mortality: Systematic Review and Meta-Analysis. Environment International, 142, Article ID: 105876. [Google Scholar] [CrossRef] [PubMed]
[9] Xiao, Q., Geng, G., Xue, T., Liu, S., Cai, C., He, K., et al. (2021) Tracking Pm2.5 and O3 Pollution and the Related Health Burden in China 2013-2020. Environmental Science & Technology, 56, 6922-6932. [Google Scholar] [CrossRef] [PubMed]
[10] Feng, Z., Sun, J., Wan, W., Hu, E. and Calatayud, V. (2014) Evidence of Widespread Ozone-Induced Visible Injury on Plants in Beijing, China. Environmental Pollution, 193, 296-301. [Google Scholar] [CrossRef] [PubMed]
[11] 郑旭曼. 基于集成学习的O3浓度逐小时预测模型研究[D]: [硕士学位论文]. 上海: 华东师范大学, 2018.
[12] 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.
[13] 景琼琼, 吕爱丽. 临汾市近地面臭氧污染特征及与气象条件的关系[J]. 山西气象, 2022(3): 121-123.
[14] 严加琪. 基于数据挖掘的臭氧时空分布特征分析及趋势预测研究[D]: [硕士学位论文]. 淮南: 安徽理工大学, 2020.[CrossRef
[15] 李金龙, 张其苏, 唐孝炎, 等. 兰州西固地区光化学烟雾污染气质模式[J]. 环境科学学报, 1988(2): 125-130.
[16] Lefohn, A.S., Shadwick, D. and Oltmans, S.J. (2010) Characterizing Changes in Surface Ozone Levels in Metropolitan and Rural Areas in the United States for 1980-2008 and 1994-2008. Atmospheric Environment, 44, 5199-5210. [Google Scholar] [CrossRef
[17] Wang, T., Ding, A., Gao, J. and Wu, W.S. (2006) Strong Ozone Production in Urban Plumes from Beijing, China. Geophysical Research Letters, 33, Article ID: 21806. [Google Scholar] [CrossRef
[18] 王丹雨, 朱媛君, 杨晓晖. 收敛交叉映射方法及其在生态学中的应用[J]. 应用生态学报, 2021, 32(12): 4539-4548.
[19] Ye, H. (2015) Nonlinear Tools for a Nonlinear World: Applications of Empirical Dynamic Modeling to Marine Ecosystems. Master’s Thesis, University of California, San Diego.
[20] Clark, A.T., Ye, H., Isbell, F., Deyle, E.R., Cowles, J., Tilman, G.D., et al. (2015) Spatial Convergent Cross Mapping to Detect Causal Relationships from Short Time Series. Ecology, 96, 1174-1181. [Google Scholar] [CrossRef] [PubMed]
[21] Sugihara, G., May, R., Ye, H., Hsieh, C., Deyle, E., Fogarty, M., et al. (2012) Detecting Causality in Complex Ecosystems. Science, 338, 496-500. [Google Scholar] [CrossRef] [PubMed]
[22] 逯艳丽. 临汾市大气臭氧污染特征及治理分析 [J]. 中国资源综合利用, 2024, 42(1): 131-134.
[23] Brönnimann, S. and Neu, U. (1997) Weekend-weekday Differences of Near-Surface Ozone Concentrations in Switzerland for Different Meteorological Conditions. Atmospheric Environment, 31, 1127-1135. [Google Scholar] [CrossRef
[24] 宁一. 2019-2021年临汾市臭氧污染特征及来源分析[D]: [硕士学位论文]. 太原: 中北大学, 2022.
[25] Li, L., Chen, C.H., Huang, C., Huang, H.Y., Zhang, G.F., Wang, Y.J., et al. (2012) Process Analysis of Regional Ozone Formation over the Yangtze River Delta, China Using the Community Multi-Scale Air Quality Modeling System. Atmospheric Chemistry and Physics, 12, 10971-10987. [Google Scholar] [CrossRef
[26] 宁一, 孙洁亚, 薛志钢, 等. 受焦化影响的下风向城区臭氧污染特征及潜在源区分析[J]. 环境工程技术学报, 2022, 12(3): 710-717.