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不同传输通道下珠江三角洲臭氧与前体物非线性响应关系
引用本文:伍永康,陈伟华,颜丰华,毛敬英,袁斌,王伟文,王雪梅. 不同传输通道下珠江三角洲臭氧与前体物非线性响应关系[J]. 环境科学, 2022, 43(1): 160-169. DOI: 10.13227/j.hjkx.202104141
作者姓名:伍永康  陈伟华  颜丰华  毛敬英  袁斌  王伟文  王雪梅
作者单位:暨南大学环境与气候研究院,粤港澳环境质量协同创新联合实验室,广州 510443
基金项目:国家重点研发计划项目(2019YFE0106300,20017YFC0210105);国家自然科学基金项目(41905086,42077205,41425020);中国博士后科学基金项目(2020M683174);国家环境保护区域空气质量监测重点实验室开放基金项目(SRAQM02202001);暨南大学高性能计算公共服务平台项目
摘    要:高度城市化的珠三角地区臭氧污染频发,臭氧污染的非线性、区域性以及气象过程影响使臭氧精确防控面临巨大挑战.本研究利用臭氧源解析技术OSAT,分析不同传输通道下珠三角臭氧敏感区分布差异,量化城市间的臭氧传输贡献,并通过敏感性试验,探讨珠三角及典型城市的臭氧污染控制策略.结果表明,静风条件下,VOCs敏感区集中在珠三角中部城...

关 键 词:珠江三角洲(PRD)  臭氧污染  传输通道  臭氧生成敏感性  来源解析
收稿时间:2021-04-15
修稿时间:2021-06-05

Nonlinear Response Relationship Between Ozone and Precursor Emissions in the Pearl River Delta Region Under Different Transmission Channels
WU Yong-kang,CHEN Wei-hu,YAN Feng-hu,MAO Jing-ying,YUAN Bin,WANG Wei-wen,WANG Xue-mei. Nonlinear Response Relationship Between Ozone and Precursor Emissions in the Pearl River Delta Region Under Different Transmission Channels[J]. Chinese Journal of Environmental Science, 2022, 43(1): 160-169. DOI: 10.13227/j.hjkx.202104141
Authors:WU Yong-kang  CHEN Wei-hu  YAN Feng-hu  MAO Jing-ying  YUAN Bin  WANG Wei-wen  WANG Xue-mei
Affiliation:Guangdong-Hongkong-Macau Joint Laboratory of Collaborative Innovation for Environmental Quality, Institution for Environmental and Climate Research, Jinan University, Guangzhou 510443, China
Abstract:With the rapid development of urbanization, ozone (O3) pollution is an ongoing occurrence in the Pearl River Delta (PRD) region in China. The effective control of O3 pollution is a great challenge owing to the nonlinear relationship between O3 and precursor emissions and the effect of meteorological conditions. Based on the regional air quality model CAMx-OSAT (ozone source apportionment technology), O3 formation regimes were determined, and inter-city transportation across PRD was quantified under different transmission channels. The results showed that spatial differences were observed for the O3 formation regimes under different transmission channels. The VOCs-sensitive regime was mainly located in the central areas of the PRD region, and the NOx-sensitive regime was distributed in the suburban areas of the PRD regions under calm wind conditions. When the northeast wind was prevailing, the polluted air mass of the urban agglomeration was transmitted southwesterly downward, resulting in the downwind areas being transformed to VOCs-sensitive; the upwind areas were still NOx-sensitive. Under the southeast wind, the VOCs-sensitive regime had a banding distribution along the southeast-northwest direction, and the remaining areas were NOx-sensitive. With the influence of transmission channels, downwind cities were significantly affected by the transmission of upwind urban agglomerations (41%-87%), whereas the local formation was the main contributor under the calm wind conditions (60%-87%). To explore the relationship between O3 and precursor emissions, a series of sensitivity tests were designed. The results showed that maximized areas (20%-36%) with reductions in O3 can be achieved by reducing VOCs and NOx in the corresponding sensitive regimes, and the maximized level with the reduction in O3 can be fulfilled by reducing VOCs in the VOCs-sensitive regime. For the typical city Jiangmen, the area that met the standard increased the most under the calm wind (11%) and southeast wind (8%) conditions when VOCs and NOx were reduced in the corresponding sensitive regimes. Additionally, under northeast wind conditions, reducing VOCs in the VOCs-sensitive regime can more effectively control O3, as the area up to the standard increased by 140%.
Keywords:Pearl River Delta (PRD)  ozone pollution  transmission channels  ozone sensitivity  source apportionment
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