Waring Michael S, Wells J Raymond
Drexel University, Department of Civil, Architectural and Environmental Engineering, 3141 Chestnut St., Philadelphia, PA 19104, United States.
Exposure Assessment Branch, Health Effects Laboratory Division, National Institute for Occupational Safety and Health, 1095 Willowdale Road, Morgantown, WV 26505, United States.
Atmos Environ (1994). 2015 Apr;106:382-391. doi: 10.1016/j.atmosenv.2014.06.062.
Indoor chemistry may be initiated by reactions of ozone (O), the hydroxyl radical (OH), or the nitrate radical (NO) with volatile organic compounds (VOC). The principal indoor source of O is air exchange, while OH and NO formation are considered as primarily from O reactions with alkenes and nitrogen dioxide (NO), respectively. Herein, we used time-averaged models for residences to predict O, OH, and NO concentrations and their impacts on conversion of typical residential VOC profiles, within a Monte Carlo framework that varied inputs probabilistically. We accounted for established oxidant sources, as well as explored the importance of two newly realized indoor sources: () the photolysis of nitrous acid (HONO) indoors to generate OH and () the reaction of stabilized Criegee intermediates (SCI) with NO to generate NO. We found total VOC conversion to be dominated by reactions both with O, which almost solely reacted with d-limonene, also with OH, which reacted with d-limonene, other terpenes, alcohols, aldehydes, and aromatics. VOC oxidation rates increased with air exchange, outdoor O, NO and d-limonene sources, and indoor photolysis rates; and they decreased with O deposition and nitric oxide (NO) sources. Photolysis was a strong OH formation mechanism for high NO, NO, and HONO settings, but SCI/NO reactions weakly generated NO except for only a few cases.
室内化学反应可能由臭氧(O)、羟基自由基(OH)或硝酸根自由基(NO)与挥发性有机化合物(VOC)的反应引发。室内O的主要来源是空气交换,而OH和NO的形成分别主要被认为是由O与烯烃和二氧化氮(NO₂)的反应产生的。在此,我们使用住宅的时间平均模型,在一个概率性改变输入的蒙特卡洛框架内,预测O、OH和NO的浓度及其对典型住宅VOC谱转化的影响。我们考虑了已确定的氧化剂来源,并探讨了两个新发现的室内来源的重要性:(1)室内亚硝酸(HONO)的光解产生OH,以及(2)稳定的克里吉中间体(SCI)与NO反应产生NO₂。我们发现总VOC转化主要由与O的反应主导,O几乎只与d-柠檬烯反应,同时也由与OH的反应主导,OH与d-柠檬烯、其他萜烯、醇类、醛类和芳烃反应。VOC氧化速率随着空气交换、室外O₃、NO₂和d-柠檬烯来源以及室内光解速率的增加而增加;随着O₃沉积和一氧化氮(NO)来源的增加而降低。对于高NO₂、NO和HONO环境,光解是一种强烈的OH形成机制,但除少数情况外,SCI/NO₂反应微弱地产生NO₂。