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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2023, Vol. 17 Issue (11) : 138    https://doi.org/10.1007/s11783-023-1738-5
RESEARCH ARTICLE
Elucidate long-term changes of ozone in Shanghai based on an integrated machine learning method
Jin Xue1,2, Fangting Wang1,2, Kun Zhang1,2, Hehe Zhai1,2, Dan Jin3, Yusen Duan3(), Elly Yaluk1,2, Yangjun Wang1,2, Ling Huang1,2, Yuewu Li3, Thomas Lei4, Qingyan Fu3, Joshua S. Fu5, Li Li1,2()
1. School of Environmental and Chemical Engineering, Shanghai University, Shanghai 200444, China
2. Key Laboratory of Organic Compound Pollution Control Engineering (MOE), Shanghai University, Shanghai 200444, China
3. Shanghai Environmental Monitoring Center, Shanghai 200235, China
4. Institute of Science and Environment, University of Saint Joseph, Macao 999078, China
5. Department of Civil and Environmental Engineering, University of Tennessee, Knoxville, TN 37996, USA
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Abstract

● A novel integrated machine learning method to analyze O3 changes is proposed.

● Various factors affecting long-term changes of O3 in Shanghai are quantified.

● Meteorological, photochemical, and regional background O3 are well separated.

Surface ozone (O3) is influenced by regional background and local photochemical formation under favorable meteorological conditions. Understanding the contribution of these factors to changes in O3 is crucial to address the issue of O3 pollution. In this study, we propose a novel integrated method that combines random forest, principal component analysis, and Shapley additive explanations to distinguish observed O3 into meteorologically affected ozone (O3_MET), chemically formed from local emissions (O3_LC), and regional background ozone (O3_RBG). Applied to three typical stations in Shanghai during the warm season from 2013 to 2021, the results indicate that O3_RBG in Shanghai was 48.8 ± 0.3 ppb, accounting for 79.6%–89.4% at different sites, with an overall declining trend of 0.018 ppb/yr. O3_LC at urban and regional sites ranged from 5.9–9.0 ppb and 8.9–14.6 ppb, respectively, which were significantly higher than the contributions of 2.5–7.4 ppb at an upwind background site. O3_MET can be categorized into those affecting O3 photochemical generation and those changing O3 dispersion conditions, with absolute contributions to O3 ranging from 13.4–19.0 ppb and 13.1–13.7 ppb, respectively. We found that the O3 rebound in 2017, compared to 2013, was primarily influenced by unfavorable O3 dispersion conditions and unbalanced emission reductions; while the O3 decline in 2021, compared to 2017, was primarily influenced by overall favorable meteorological conditions and further emissions reduction. These findings highlight the challenge of understanding O3 change due to meteorology and regional background, emphasizing the need for systematic interpretation of the different components of O3.

Keywords Ozone      Integrated method      Machine learning     
Corresponding Author(s): Yusen Duan,Li Li   
About author:

* These authors contributed equally to this work.

Issue Date: 15 November 2023
 Cite this article:   
Jin Xue,Fangting Wang,Kun Zhang, et al. Elucidate long-term changes of ozone in Shanghai based on an integrated machine learning method[J]. Front. Environ. Sci. Eng., 2023, 17(11): 138.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-023-1738-5
https://academic.hep.com.cn/fese/EN/Y2023/V17/I11/138
Fig.1  Framework of the Integrated Method.
Fig.2  Time series of O3, maximum daily 8 hour average ozone (MDA8 O3) and NO2 at PT (blue), DSL (red), PDHN (green). In the left figure, the thick line is the 360-day sliding average; the thin line is the daily average. In the right figure; the shaded area is the 95% confidence interval of corresponding data.
Fig.3  Bivariate polar plot and wind rose at PT, DSL and PDHN.
Fig.4  Comparisons of the major meteorological factors among the three observational sites.
Fig.5  Meteorological contributions to O3 at PT, DSL and PDHN. The bands beside the lines are the 95% confidence intervals in panel (a). Base is the base value of the SHAP approach, i.e. the average of the SHAP value in panels (b–d).
Fig.6  Contributions of O3_RBG at PT, DSL and PDHN. In panel (a), the upper and lower boundaries of the box represent the 25th percentile and 75th percentile, and the notches represent the confidence interval around the median. The line and hollow triangles inside boxes represent the average and median values of corresponding data, respectively. The error lines above and below the box represent the 25th percentile value minus 1.5 * IQR (interquartile range) and the 75th percentile value plus 1.5 * IQR (interquartile range), respectively. In panel (b), the error line indicates the 95% confidence interval of the corresponding data.
Fig.7  Contributions of O3_LC at (a) PT, (b) DSL and (c) PDHN. In panels (a–c), the upper and lower boundaries of the box represent the 25th percentile and 75th percentile, and the notches represent the confidence interval around the median. The line and hollow triangles inside boxes represent the average and median values of corresponding data, respectively. The error lines above and below the box represent the 25th percentile value minus 1.5 * IQR (interquartile range) and the 75th percentile value plus 1.5 * IQR (interquartile range), respectively. In panels (d–f), the error line indicates the 95% confidence interval of the corresponding data.
Fig.8  Quantification of influencing factors on O3 changes during the warm season from 2013 to 2021 in Shanghai.
Fig.9  Variation of influencing factors on O3 for typical years at PT (a), DSL (b) and PDHN (c).
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