Chao-Long Wang, Lian Xue, Yi-Sheng Zhang, Xiao-Fei Qin, Yuan Fang, Wen-Xin Tao, Jin-Hua Du, Su-Fan Zhang, Guan Wang, Da-Sa Gu, Shan-Shan Cui
{"title":"[Urban Ozone Driving Factors Based on Explainable Machine Learning].","authors":"Chao-Long Wang, Lian Xue, Yi-Sheng Zhang, Xiao-Fei Qin, Yuan Fang, Wen-Xin Tao, Jin-Hua Du, Su-Fan Zhang, Guan Wang, Da-Sa Gu, Shan-Shan Cui","doi":"10.13227/j.hjkx.202404320","DOIUrl":null,"url":null,"abstract":"<p><p>Sixteen sites in the coastal city of Qingdao, including eight national control sites, seven provincial control sites, and one background site, were selected. By coupling the extreme gradient boosting (XGBoost) model with the interpretability SHapley Additive exPlanations (SHAP) module, the impact of meteorological elements and atmospheric pollutant emissions on ozone (O<sub>3</sub>) pollution was investigated. The results indicated that from 2019 to 2023, meteorological factors contributed 67.7% to O<sub>3</sub> formation, whereas emissions from atmospheric pollutants accounted for 32.3%. Surface solar radiation significantly affected O<sub>3</sub> formation from 10:00 to 17:00. A positive correlation existed between temperature and O<sub>3</sub> concentration, peaking at 14:00. A relative humidity below 70% was conducive to O<sub>3</sub> formation and a relative humidity above 70% had a 94% probability of negatively contributing to O<sub>3</sub> production. Particularly between 12:00 and 16:00, relative humidity significantly and positively contributed to O<sub>3</sub> formation. When the boundary layer height was below 500 meters, it positively affected O<sub>3</sub> concentration, whereas above this height, its impact weakened. In the morning and late afternoon, boundary layer height promoted the formation of O<sub>3</sub> concentration. Easterly (E) to southwesterly (SW) winds had a positive effect on O<sub>3</sub> concentrations in Qingdao. NO<sub>2</sub> showed a negative response in the morning (06:00-11:00) and a positive response in the afternoon (12:00-15:00). PM<sub>2.5</sub> had a nonlinear positive correlation with O<sub>3</sub>, positively affecting O<sub>3</sub> concentration from 07:00 to 14:00 PM and suppressing it from 15:00 to 18:00. Significant differences existed in the dominant factors of O<sub>3</sub> concentration across different areas and seasons. In the western Laoshan District, Yangkou, the western site of the Shinan District, and eastern and western parts of the West Coast New Area, surface solar radiation had a noticeably lower impact on O<sub>3</sub> than in other locations. The effect of NO<sub>2</sub> was most significant in the eastern parts of the West Coast New Area, western Laoshan District, and Yangkou. PM<sub>2.5</sub> affected O<sub>3</sub> formation more in these sites than in others of Qingdao. In spring, the impact of NO<sub>2</sub> was more significant in the western Laoshan and Shinan Districts. In summer, surface solar radiation was more influential in Yangkou, the eastern and western parts of the West Coast New Area, the western Laoshan District, and the Shibei District, whereas, relative humidity was the key factor in other locations. In autumn, temperature and surface solar radiation were the main factors affecting O<sub>3</sub>. In winter, the contribution of NO<sub>2</sub> was higher than that in different seasons, with anthropogenic emissions playing a more important role in O<sub>3</sub> formation. The analysis of days exceeding O<sub>3</sub> standards showed that surface solar radiation and NO<sub>2</sub> were the main drivers of exceeding O<sub>3</sub> concentrations. For all sites, the total SHAP values of PM<sub>2.5</sub> and PM<sub>10</sub> on days exceeding O<sub>3</sub> standards ranged between 6.1 μg·m<sup>-3</sup> and 12.4 μg·m<sup>-3</sup>.</p>","PeriodicalId":35937,"journal":{"name":"环境科学","volume":"46 5","pages":"2642-2653"},"PeriodicalIF":0.0000,"publicationDate":"2025-05-08","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"环境科学","FirstCategoryId":"1087","ListUrlMain":"https://doi.org/10.13227/j.hjkx.202404320","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q2","JCRName":"Environmental Science","Score":null,"Total":0}
引用次数: 0
Abstract
Sixteen sites in the coastal city of Qingdao, including eight national control sites, seven provincial control sites, and one background site, were selected. By coupling the extreme gradient boosting (XGBoost) model with the interpretability SHapley Additive exPlanations (SHAP) module, the impact of meteorological elements and atmospheric pollutant emissions on ozone (O3) pollution was investigated. The results indicated that from 2019 to 2023, meteorological factors contributed 67.7% to O3 formation, whereas emissions from atmospheric pollutants accounted for 32.3%. Surface solar radiation significantly affected O3 formation from 10:00 to 17:00. A positive correlation existed between temperature and O3 concentration, peaking at 14:00. A relative humidity below 70% was conducive to O3 formation and a relative humidity above 70% had a 94% probability of negatively contributing to O3 production. Particularly between 12:00 and 16:00, relative humidity significantly and positively contributed to O3 formation. When the boundary layer height was below 500 meters, it positively affected O3 concentration, whereas above this height, its impact weakened. In the morning and late afternoon, boundary layer height promoted the formation of O3 concentration. Easterly (E) to southwesterly (SW) winds had a positive effect on O3 concentrations in Qingdao. NO2 showed a negative response in the morning (06:00-11:00) and a positive response in the afternoon (12:00-15:00). PM2.5 had a nonlinear positive correlation with O3, positively affecting O3 concentration from 07:00 to 14:00 PM and suppressing it from 15:00 to 18:00. Significant differences existed in the dominant factors of O3 concentration across different areas and seasons. In the western Laoshan District, Yangkou, the western site of the Shinan District, and eastern and western parts of the West Coast New Area, surface solar radiation had a noticeably lower impact on O3 than in other locations. The effect of NO2 was most significant in the eastern parts of the West Coast New Area, western Laoshan District, and Yangkou. PM2.5 affected O3 formation more in these sites than in others of Qingdao. In spring, the impact of NO2 was more significant in the western Laoshan and Shinan Districts. In summer, surface solar radiation was more influential in Yangkou, the eastern and western parts of the West Coast New Area, the western Laoshan District, and the Shibei District, whereas, relative humidity was the key factor in other locations. In autumn, temperature and surface solar radiation were the main factors affecting O3. In winter, the contribution of NO2 was higher than that in different seasons, with anthropogenic emissions playing a more important role in O3 formation. The analysis of days exceeding O3 standards showed that surface solar radiation and NO2 were the main drivers of exceeding O3 concentrations. For all sites, the total SHAP values of PM2.5 and PM10 on days exceeding O3 standards ranged between 6.1 μg·m-3 and 12.4 μg·m-3.