State Key Laboratory of Severe Weather & Key Laboratory of Atmospheric Chemistry of CMA, Chinese Academy of Meteorological Sciences, Beijing 100081, China; Collaborative Innovation Center of Atmospheric Environment and Equipment Technology, Jiangsu Key Laboratory of Atmospheric Environment Monitoring and Pollution Control (AEMPC), Nanjing University of Information Science & Technology, Nanjing 210044, China.
Jiangxi Ecological Meteorology Center, Nanchang 330096, Jiangxi, China.
Sci Total Environ. 2020 May 20;718:137388. doi: 10.1016/j.scitotenv.2020.137388. Epub 2020 Feb 19.
Although atmospheric peroxyacetyl nitrate (PAN) and O have been extensively measured in Beijing during the summertime, the abundances of PAN, peroxypropionyl nitrate (PPN) and the total odd-reactive nitrogen budget (NO) and their inter-relationship have been studied comparatively less in the winter. Here we measured atmospheric PAN, PPN, O, NO, and NO in Beijing from Nov. 2012 to Jan. 2013. Compared with our previous results in the summertime, much lower levels were observed in the winter, with the mean and maximum values of 311.8 and 1465 pptv for PAN, 52.8 and 850.6 pptv for PPN, and 11.6 and 36.7 ppbv for O. In contrast, high levels were found as 94.2 and 374.9 ppbv for NO, with a major constituent of NO (75.9%). The source to the west and northwest made the significant contribution to the relatively high O concentrations during nighttime. PAN concentrations were highly related with the PAN-rich air mass transported from the southeast during the nighttime, whereas predominated by local photochemical production during the daylight. The distributions of NO and NO were dominated by local emission and photochemical production during daylight but also influenced by air masses transported from south direction during nighttime. Significant positive correlation (R = 0.9, p < 0.0001) between PAN and PPN with a slope (∆PPN/∆PAN) of 0.17 indicated that anthropogenic volatile organic compounds (AVOCs) dominated the photochemical formation of PANs in Beijing, and the independent relationship between the PPN/PAN ratio and PAN (>500 pptv) implied a steady state between PAN and PPN achieving rapidly in the polluted air masses. Negative correlation and slopes between PAN and O likely resulted from their weak photochemical productions in the winter, coupled with the large NO sources which acted as a local sink for O, but much less so for PAN due to its enhanced thermal stability under low temperature.
尽管大气过氧乙酰硝酸酯 (PAN) 和 O 在夏季已在北京广泛测量,但 PAN、过氧丙酰硝酸酯 (PPN) 的丰度以及总奇数反应性氮预算 (NO) 及其相互关系在冬季的研究相对较少。在这里,我们从 2012 年 11 月至 2013 年 1 月测量了北京大气中的 PAN、PPN、O、NO 和 NO。与我们以前在夏季的结果相比,冬季的水平要低得多,其平均值和最大值分别为 PAN 为 311.8 和 1465 pptv,PPN 为 52.8 和 850.6 pptv,O 为 11.6 和 36.7 ppbv。相比之下,NO 的高浓度为 94.2 和 374.9 ppbv,其中 75.9%为 NO。来自西部和西北部的污染源使得夜间 O 浓度相对较高。夜间,来自东南部的富含 PAN 的气团输送导致 PAN 浓度升高,而白天主要由当地光化学产生。NO 和 NO 的分布在白天主要由当地排放和光化学产生控制,但夜间也受来自南方的气团输送影响。PAN 和 PPN 之间存在显著正相关(R=0.9,p<0.0001),斜率(∆PPN/∆PAN)为 0.17,表明北京大气中 PAN 的光化学形成主要由人为挥发性有机化合物(AVOCs)控制,且 PPN/PAN 比与 PAN (>500 pptv) 的独立关系表明在污染空气团中 PAN 和 PPN 之间很快达到了平衡。PAN 和 O 之间的负相关和斜率可能是由于冬季它们的光化学产生较弱,加上大量的 NO 源作为 O 的本地汇,但由于其在低温下增强的热稳定性,对 PAN 的影响要小得多。