与珠江三角洲典型工业园区释放的挥发性有机化合物(VOCs)和氮氧化物(NOX)有关的臭氧形成潜力†。

IF 2.8 Q3 ENVIRONMENTAL SCIENCES
Taicheng An, Jiajia Li, Qinhao Lin and Guiying Li
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引用次数: 0

摘要

臭氧(O3)污染已被认为是华南珠江三角洲(PRD)地区的主要空气污染。了解 O3 的形成对挥发性有机化合物(VOC)和氮氧化物(NOX)限制机制的敏感性是缓解 O3 污染的关键一步。在此,我们于 2020 年 6 月在珠三角地区一个工业园区的多个采样点同时测量了挥发性有机化合物、氮氧化物和臭氧。VOCs/NOX 比率介于 0.5 至 5.7 之间,表明该工业园区的 O3 形成受 VOC 限制。挥发性有机化合物的 O3 形成潜能估计值(OFP)显示,机动车和工业源产生的烯烃和芳香烃分别占工业园区 O3 形成的 40% 和 39%。然而,在估算出高 OFP 值(194 ppb)的区域,观测到的 O3 水平较低(50 ppb)。进一步分析发现,高 O3 区域的 NOx 浓度(25 ± 10 ppb)低于低 O3 区域的 NOx 浓度(36 ± 6 ppb),这主要是由于 NO 与 O3 发生滴定反应生成 NO2,从而导致 O3 的消耗。这一结果意味着 NOX 控制不利于研究区域的 O3 污染。因此,研究区域的 O3 污染控制应考虑 NOX 滴定和控制 VOC 排放的效果。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Ozone formation potential related to the release of volatile organic compounds (VOCs) and nitrogen oxide (NOX) from a typical industrial park in the Pearl River Delta†

Ozone formation potential related to the release of volatile organic compounds (VOCs) and nitrogen oxide (NOX) from a typical industrial park in the Pearl River Delta†

Ozone (O3) pollution has been recognized as the major air pollution in the Pearl River Delta (PRD) region, South China. Understanding O3 formation sensitive to volatile organic compound (VOC)- and nitrogen oxide (NOX)-limited regimes is a key step for alleviating O3 pollution. Herein, measurements of VOCs, NOX and O3 were simultaneously performed at multi sampling sites in an industrial park of the PRD region during June, 2020. VOCs/NOX ratios ranged from 0.5 to 5.7, suggesting that the O3 formation was in the VOC-limited regime in the industrial park. The estimated O3 formation potential (OFP) of VOCs showed that alkenes and aromatic hydrocarbons from motor vehicles and industrial sources contributed to 40% and 39% of the O3 formation, respectively, in the industrial park. However, a low O3 level (<50 ppb) was observed in the region where high OFP values (>194 ppb) were estimated. Further analysis found that the concentration of NOx (25 ± 10 ppb) in the high O3 region was lower than that (36 ± 6 ppb) in the low O3 region, mostly due to the titration reaction of NO and O3 to form NO2, therefore leading to the consumption of O3. This result implies that NOX control was not conducive to the O3 pollution in the study region. Thus, O3 pollution control in the study region should be taken into consideration in terms of the effect of NOX titration and control of VOC emissions.

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