首页> 外文期刊>Atmospheric Chemistry and Physics Discussions >Characterization of submicron particles by time-of-flight aerosol chemical speciation monitor (ToF-ACSM) during wintertime: aerosol composition, sources, and chemical processes in Guangzhou, China
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Characterization of submicron particles by time-of-flight aerosol chemical speciation monitor (ToF-ACSM) during wintertime: aerosol composition, sources, and chemical processes in Guangzhou, China

机译:冬季飞行时间气溶胶化学品质监测仪(TOF-ACSM)的亚微米粒子的表征:中国广州的气溶胶组成,来源和化学过程

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Particulate matter (PM) pollution in China is an emerging environmental issue which policy makers and the public have increasingly paid attention to. In order to investigate the characteristics, sources, and chemical processes of PM pollution in Guangzhou, field measurements were conducted from 20?November 2017 to 5?January 2018, with a time-of-flight aerosol chemical speciation monitor (ToF-ACSM) and other collocated instruments. Mass concentrations of non-refractory submicron particulate matter (NR-PM1) measured by the ToF-ACSM correlated well with those of PM2.5 or PM1.1 measured by filter-based methods. The organic mass fraction increased from 45% to 53% when the air switched from non-pollution periods to pollution episodes (EPs), indicating significant roles of organic aerosols (OAs) during the whole study. Based on the mass spectra measured by the ToF-ACSM, positive matrix factorization (PMF) with the multilinear engine (ME-2) algorithm was performed to deconvolve OA into four factors, including hydrocarbon-like OA (HOA, 12%), cooking OA (COA, 18%), semi-volatile oxygenated OA (SVOOA, 30%), and low-volatility oxygenated OA (LVOOA, 40%). Furthermore, we found that SVOOA and nitrate were significantly contributed from local traffic emissions while sulfate and LVOOA were mostly attributed to regional pollutants. Comparisons between this work and other previous studies in China show that secondary organic aerosol (SOA) fraction in total OA increases spatially across China from the north to the south. Two distinctly opposite trends for NR-PM1 formation were observed during non-pollution periods and pollution EPs. The ratio of secondary PM (SPM= SVOOA+LVOOA+sulfate+nitrate+ammonium) to primary PM (PPM=HOA+COA+chloride), together with peroxy radicals RO2? and ozone, increased with increasing NR-PM1 concentration during non-pollution periods, while an opposite trend of these three quantities was observed during pollution EPs. Furthermore, oxidation degrees of both OA and SOA were investigated using the f44∕f43 space and the results show that at least two OOA factors are needed to cover a large range of f44 and f43 in Guangzhou. Comparisons between our results and other laboratory studies imply that volatile organic compounds (VOCs) from traffic emissions, in particular from diesel combustion and aromatic compounds, are the most likely SOA precursors in Guangzhou. Peroxy radical RO2? was used as a tracer for SOA formed through gas-phase oxidation. For non-pollution periods, SOA concentration was reasonably correlated with RO2? concentration during both daytime and nighttime, suggesting that gas-phase oxidation was primarily responsible for SOA formation. However, there was no correlation between SOA and RO2? in pollution EPs, suggesting a dramatically changed mechanism for SOA formation. This conclusion can also be supported by different features of SOA in a van Krevelen diagram between non-pollution periods and pollution EPs. Furthermore, for pollution EPs, when NR-PM1 mass concentration was divided into six segments, in each segment except for the lowest one SOA concentration was correlated moderately with RO2? concentration, suggesting that gas-phase oxidation still plays important roles in SOA formation. The intercepts of the above linear regressions, which likely correspond to the extent of other mechanisms (i.e., heterogeneous and multiphase reactions), increase with increasing NR-PM1 mass concentration. Our results suggest that while gas-phase oxidation contributes predominantly to SOA formation during non-pollution periods, other mechanisms such as heterogeneous and multiphase reactions play more important roles in SOA formation during pollution EPs than gas-phase oxidation.
机译:中国颗粒物(PM)污染是一个新兴的环境问题,政策制定者和公众越来越受到关注。为了探讨广州PM污染的特点,来源和化学过程,从20月20日进行了现场测量,2017年11月至5日?2018年1月,采用飞行时间气溶胶化学品质监测仪(TOF-ACSM)和其他并置仪器。通过TOF-ACSM测量的非难治性亚微粒颗粒物质(NR-PM1)的质量浓度与通过基于滤光剂的方法测量的PM2.5或PM1.1的孔。当空气从非污染期转换为污染发作(EPS)时,有机质量级分从45%增加到53%,表明在整个研究中有机气溶胶(OAS)的显着作用。基于通过TOF-ACSM测量的质谱,对具有多线性发动机(ME-2)算法的阳性基质分子分解(PMF)进行DecoNvolve OA分为四个因子,包括烃类OA(HOA,12%),烹饪OA(COA,18%),半挥发性含氧OA(SVOOA,30%)和低挥发性含氧OA(LVOOA,40%)。此外,我们发现SVOOA和硝酸盐显着从局部交通排放显着贡献,同时硫酸盐和LVOOA主要归因于区域污染物。这项工作与中国其他先前研究之间的比较表明,次级有机气溶胶(SOA)分数在整个中国从北部到南方的空间上增加。在非污染期和污染EPS期间观察到NR-PM1形成的两个明显相反的趋势。仲PM(SPM = SVOOA + LVOOA +硫酸盐+硝酸铵+铵)与主要PM(PPM = HOA + COA +氯化物)的比例与过氧自由基RO2?和臭氧,随着非污染期内的NR-PM1浓度增加而增加,而在污染EPS期间观察到这三种量的相反趋势。此外,使用F44 / F43空间研究了OA和SOA的氧化程度,结果表明,至少需要两个臭氧因子来涵盖广州的大量F44和F43。我们的结果和其他实验室研究之间的比较意味着来自交通排放的挥发性有机化合物(VOC),特别是来自柴油燃烧和芳族化合物,是广州最有可能的SOA前体。过氧自由基RO2?用作通过气相氧化形成的SOA的示踪剂。对于非污染期,SOA浓度与RO2合理相关?白天和夜间浓度,表明气相氧化主要负责SOA形成。但是,SOA和RO2之间没有相关性?在污染eps中,表明SOA形成的急剧改变机制。在非污染期和污染氧化钙之间的van Krevelen图中,SOA的不同特征也可以支持这一结论。此外,对于污染EPS,当NR-PM1质量浓度被分成六个区段时,在每个段中,除了最低一个SOA浓度,用RO2适度地相关?浓缩,表明气相氧化仍然在SOA形成中起重要作用。上述线性回归的截距,这可能对应于其他机制的程度(即,异质和多相反应),随着NR-PM1质量浓度的增加而增加。我们的研究结果表明,虽然气相氧化在非污染期间主要贡献到SOA形成中,但在污染EPS期间,其他机制如异质和多相反应在污染EPS期间在SOA形成中发挥更重要的作用。
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