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JIA Long, YU Shanshan, XU Yongfu. 2024. Physicochemical Processes of a Typical Ozone Pollution in Suburb of Beijing [J]. Chinese Journal of Atmospheric Sciences (in Chinese), 48(1): 391−404. DOI: 10.3878/j.issn.1006-9895.2311.23309
Citation: JIA Long, YU Shanshan, XU Yongfu. 2024. Physicochemical Processes of a Typical Ozone Pollution in Suburb of Beijing [J]. Chinese Journal of Atmospheric Sciences (in Chinese), 48(1): 391−404. DOI: 10.3878/j.issn.1006-9895.2311.23309

Physicochemical Processes of a Typical Ozone Pollution in Suburb of Beijing

  • Ozone (O3) pollution is currently a major environmental problem in some cities in China. O3 formation depends on chemical reactions influenced by atmospheric physical processes and various meteorological conditions. Therefore, it is necessary to study near-ground O3 pollution from both chemical and physical aspects. This study analyzed the physicochemical processes of photochemical pollution in Huairou, an urban city in Beijing, during autumn 2022. The analysis combines field observations and Eulerian photochemical box model simulations. Daily variations in meteorological factors (such as temperature, relative humidity, and wind speed) and concentrations of O3 and its precursors including volatile organic compounds (VOCs) and nitrogen oxides (NOx, x=1, 2) were determined. Source analysis revealed that the primary sources of VOCs are traffic emissions (46%), plant sources (25%), solvent evaporation (23%), and combustion processes (9%). The contribution of O3 from regional transport and the reactions of local VOCs were obtained using the Euler photochemical box model. The results indicate that O3 is primarily from horizontal transport (>74%) during the strong north wind prevailing period. During weak south or southeast winds, O3 is formed primarily through VOC and NOx photochemical reactions. Based on the O3 formation potential of VOCs, alkenes contribute the most to O3 formation (67%), followed by aromatics (16%). Sensitivity analysis revealed that O3 formation is most sensitive to physical factors, such as light intensity, temperature, and boundary layer height, with reactive alkenes being the most sensitive among VOCs. Finally, O3 pollution control strategies are suggested based on the Empirical Kinetics Modeling Approach (EKMA) curves.
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