School of Environmental and Chemical Engineering, Shanghai University, Shanghai 200444, China.
State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China.
Environ Pollut. 2024 Nov 1;360:124627. doi: 10.1016/j.envpol.2024.124627. Epub 2024 Jul 26.
Ozone (O) concentrations usually peak at midday by photochemical reactions and gradually decline after sunset due to chemical destruction and dry deposition. However, an increase in the frequency of elevated nocturnal ozone enhancement (NOE) and high nocturnal ozone value (HNOV) has been frequently observed in urban areas of eastern China, but the reasons are not well understood. In this study, taking a typical industrial city, ZiBo as a case study, we analyzed the trends, characteristics, and causes of the NOE and HNOV events in historical years by combining observations and model simulations. During the warm season (April-September) of 2017-2023, HNOV events are accompanied by low humidity, high temperature, large friction velocity, and a high boundary layer (52 days in total), whereas NOE events coincide with increases in humidity, wind speed, friction velocity, and boundary layer height (141 days in total). During the HNOV and NOE events, the nighttime average concentrations of O were 77 ± 7 and 12 ± 6 μg m higher than the non-nocturnal O period, indicating enhanced atmospheric oxidizing capacity during nighttime. The modeling results indicate that both the HNOV and NOE events were mainly driven by vertical mixing and regional transport. We selected a typical period with high O pollution and frequent NOE and HNOV events to conduct the modeling study. Three typical nocturnal O events are identified: Case I was mainly driven by horizontal transport; while in the two subsequent cases, the vertical transport contribution was 80 μg m h (20:00 LT on June 21, 2021) and 35 μg m h (02:00 LT on June 26, 2021), respectively. Our study reveals that the O pollution in industrial cities has been extending to nighttime, primarily attributed to vertical mixing and horizontal transport within the boundary layer. This highlights the critical role of implementing regional joint control action to reduce primary emissions and eliminate residual ozone.
臭氧(O)浓度通常通过光化学反应在中午达到峰值,并在日落之后由于化学破坏和干沉降而逐渐下降。然而,在中国东部的城市地区,夜间臭氧升高(NOE)和高夜间臭氧值(HNOV)的频率增加已频繁观察到,但原因尚不清楚。在这项研究中,以典型的工业城市淄博为例,我们通过结合观测和模型模拟分析了历史年份中 NOE 和 HNOV 事件的趋势、特征和原因。在 2017 年至 2023 年的暖季(4 月至 9 月),HNOV 事件伴随着低湿度、高温、大摩擦速度和高边界层(共 52 天),而 NOE 事件则伴随着湿度、风速、摩擦速度和边界层高度的增加(共 141 天)。在 HNOV 和 NOE 事件期间,夜间平均 O 浓度比非夜间 O 期高 77 ± 7 和 12 ± 6 μg m,表明夜间大气氧化能力增强。建模结果表明,HNOV 和 NOE 事件主要受垂直混合和区域输送驱动。我们选择了一个 O 污染高且频繁发生 NOE 和 HNOV 事件的典型时期进行建模研究。确定了三个典型的夜间 O 事件:案例 I 主要受水平输送驱动;而在后两个案例中,垂直输送的贡献分别为 80 μg m h(2021 年 6 月 21 日 20 时 LT)和 35 μg m h(2021 年 6 月 26 日 2 时 LT)。我们的研究表明,工业城市的 O 污染已经扩展到夜间,主要归因于边界层内的垂直混合和水平输送。这突出表明,实施区域联合控制行动以减少一次排放和消除残留臭氧的关键作用。