School of Environment and Energy, South China University of Technology, Guangzhou 510006, China.
School of Environment and Energy, South China University of Technology, Guangzhou 510006, China.
Environ Int. 2022 Jan;158:106952. doi: 10.1016/j.envint.2021.106952. Epub 2021 Oct 28.
Ground-level O pollution has been continuously worsening in China despite gradual improvement in other major pollutant levels. Understanding the sensitivity of O production to its precursors (OPS) is a prerequisite for formulating effective O control measures, but this has been hampered by significant discrepancies in OPS produced by traditional identification approaches using observation-based models (OBM) and emission-based models (EBM). In this study, by applying OBM and EBM in parallel within a month having significant O pollution in Shanghai, China, we demonstrated that a lack of carbonyl input, overestimation in NO monitoring data, and differences in simulation period and emission reduction area were the core factors leading to OPS discrepancies, and that a reliable OPS cannot be obtained unless these factors are reconciled. By collectively addressing these factors, the number of days with a consistent OPS from both models increased from 6-7 to 20-21 in a month, and the R value defined to quantify the discrepancy decreased by ∼55%. The contributions of these factors to OPS discrepancy differed greatly in urban and suburban settings, mainly caused by differences in pollutant emission and transport characteristics. Overall, OPS identified solely by OBM or EBM is associated with great uncertainty, while reliable OPS estimation can be achieved by a collective application of OBM and EBM with consensus on the above factors. The method demonstrated here could be applied to other photo-chemically active regions worldwide as part of efforts to address ozone pollution.
尽管中国其他主要污染物的水平逐渐改善,但地面臭氧污染仍在持续恶化。了解臭氧生成对其前体(OPS)的敏感性是制定有效臭氧控制措施的前提,但由于基于观测模型(OBM)和基于排放模型(EBM)的传统识别方法产生的 OPS 存在显著差异,这一目标受到了阻碍。在本研究中,通过在中国上海一个月内同时应用 OBM 和 EBM 进行臭氧污染,我们证明了缺乏羰基输入、NO 监测数据高估以及模拟期和减排区的差异是导致 OPS 差异的核心因素,除非这些因素得到协调,否则无法获得可靠的 OPS。通过综合解决这些因素,两个模型的 OPS 一致天数从一个月内的 6-7 天增加到 20-21 天,用于量化差异的 R 值下降了约 55%。这些因素对城市和郊区 OPS 差异的贡献差异很大,主要是由于污染物排放和传输特征的差异造成的。总体而言,仅通过 OBM 或 EBM 确定的 OPS 存在很大的不确定性,而通过 OBM 和 EBM 的集体应用,并就上述因素达成共识,可以实现可靠的 OPS 估计。这里展示的方法可以作为应对臭氧污染努力的一部分,应用于全球其他光化学反应活跃地区。