XIA Nan, LI Anlan, QUAN Weilin, et al. Analysis of ground-level ozone pollution and its driving factors based on GTWR in China [J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2024, 40(23): 283-293. DOI: 10.11975/j.issn.1002-6819.202405206
    Citation: XIA Nan, LI Anlan, QUAN Weilin, et al. Analysis of ground-level ozone pollution and its driving factors based on GTWR in China [J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2024, 40(23): 283-293. DOI: 10.11975/j.issn.1002-6819.202405206

    Analysis of ground-level ozone pollution and its driving factors based on GTWR in China

    • The main purpose of this research is to evaluate the effectiveness and practical performance of the spatiotemporal and temporal weighted regression model (GTWR), in order to accurately estimate the ozone (O3) concentrations across China. A GTWR model was developed and validated to estimate O3 concentrations, according to a comprehensive set of nine auxiliary variables. These variables included the ground-based O3 monitoring station, Ozone Monitoring Instrument (OMI) ozone column concentration, relative humidity, precipitation, wind speed, temperature, evapotranspiration, atmospheric boundary layer height, normalized vegetation index (NDVI), and population density. The spatial distribution patterns of O3 concentrations were analyzed using geographical detectors. A systematic investigation was then made to explore the influence of these nine driving factors on O3 levels, particularly for the impact of these interactions among these factors on the governing mechanisms of O3 distribution. The results reveal the following key points: 1) Multicollinearity and Model Performance: The nine variables shared a low level of multicollinearity, indicating the reliable performance of the model. GTWR model was achieved in a high level of accuracy over the period from 2014 to 2021, with the coefficient of determination (R2) not less than 0.81. The performance of the model also included a root mean square error (RMSE) ranging from 9.19 to 10.90 µg/m3 and a mean absolute error (MAE) between 6.27 and 7.73 µg/m3, indicating the robust predictive capabilities. 2) Trends in ozone concentrations: the annual average concentration of ozone demonstrated a general upward trend since 2014, characterized by an initial increase, a subsequent decrease, and a gradual rise. There were distinct seasonal variations in the O3 levels. The average concentrations were ranked in the descending order of summer, spring, autumn, winter. The higher O3 concentrations were observed during warmer seasons, compared with the cooler ones. The spatial distribution of O3 concentrations shared a significant regional pattern that aligned closely with the latitude. This distribution of pattern also represented the population density and economic development across China, where the higher O3 levels were concentrated in regions between 30° and 45° north latitude. 3) Geographical detector analysis: Evapotranspiration, atmospheric boundary layer height, and temperature were the strongest single factors on the O3 level, with explanatory powers of 0.840, 0.797, and 0.759, respectively. The interactions of most factors shared a dual-factor enhancement, followed by a nonlinear enhancement, indicating joint changes in O3. There was no interaction to show the linear or nonlinear weakening. All factors shared an enhancing effect on O3 concentration, albeit to varying degrees. Furthermore, the explanatory power was further improved, when the factors interacted. Among them, the strongest interactions were observed between evapotranspiration and population density, as well as the relative humidity and temperature, with explanatory values of 0.95. Therefore, there was a more pronounced impact of factor interactions on O3 concentrations, compared with single factors. Ecological detection showed significant differences between evapotranspiration, temperature, and all other factors except atmospheric boundary layer height, and between atmospheric boundary layer height and all other factors except evapotranspiration and temperature. It infers that the combined effects of evapotranspiration, atmospheric boundary layer height, and temperature with other factors posed a greater impact on the spatial distribution of ozone. Single-factor analysis also verified that these three factors shared a stronger effect on ozone. There was no significant difference between the rest factors, indicating their relatively similar mechanisms of impact on ozone concentration. In summary, the GTWR model was a robust tool to analyze the O3 concentrations, and effectively capture both spatial and temporal variations. The findings also emphasized the complex interplay between environmental variables and O3 levels. The comprehensive models were necessary to consider both the individual and interactive effects of multiple factors. This approach can provide valuable insights into the spatial distribution and temporal dynamics of O3.
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