Source profile characteristics of industrial VOCs in Shenzhen from the perspective of PM2.5 and O3 synergistic control
HUANG Pei-rong1, ZHU Bo1, ZHANG Yue1, HUANG Xiao-feng1, ZHU Qiao1, YU Guang-he2, YAN Min3, LIANG Yong-xian3, HE Ling-yan1
1. Laboratory of Atmospheric Observation Supersite, School of Environment and Energy, Peking University Shenzhen Graduate School, Shenzhen 518055, China; 2. PKU-HKUST Shenzhen-Hong Kong Institution, Shenzhen 518057, China; 3. Shenzhen Academy of Environmental Sciences, Shenzhen 518001, China
Abstract:100 VOCs components of samples were detected taken from 8 typical industries in Shenzhen so as to characterize different sources and analyze their impacts on PM2.5 and ozone pollution. The results show that, of all emissions from gas stations, alkanes accounted for 48.4%, followed by oxygenated VOCs (27.6%), ethyl acetate (14.1%), isopentane (13.0%), and n-pentane (12.0%). While oxygenated VOCs were mainly emitted from manufacture of coating, adhesives, ink, chemicals, textile printing and dyeing agents, pharmaceutical products, etc., accounting for 42.3%~97.1% of all VOCs. Furthermore, acetone was dominantly emitted from most industries and acetonitrile from some industries. For waste-to-energy industry, oxygenated VOCs and halogenated hydrocarbons contributed 33.9% and 28.3%, respectively, followed by acetaldehyde (13.4%), acetone (11.0%) and chloromethane (6.1%). For synergistically controlling PM2.5 and ozone, aromatic hydrocarbons and olefins generated from storage and transportation are the primary compounds to be mitigated; and oxygenated VOCs and aromatic hydrocarbons are the key components to be controlled in processing industry and waste disposal. Because of high SRO3 (6.0g/g) and SRSOA (1.2g/g) in coating manufacture, to most effectively mitigate PM2.5 and ozone by reducing per unit of VOCs emissions should become the priority for synergistically controlling PM2.5 and ozone in Shenzhen.
Qu Y W, Wang T J, Cai Y F, et al. Influence of atmospheric particulate matter on ozone in Nanjing, China:Observational study and mechanistic analysis[J]. Advances in Atmospheric Sciences, 2018,35(11):1381-1395.
[2]
Tan Z F, Lu K D, Jiang M Q, et al. Exploring ozone pollution in Chengdu, southwestern China:A case study from radical chemistry to O3-VOC-NOx sensitivity[J]. Science of the Total Environment, 2018,636:775-786.
[3]
Xu J, Zhang Y H, Zheng S Q, et al. Aerosol effects on ozone concentrations in Beijing:A model sensitivity study[J]. Journal of Environmental Sciences, 2012,24(4):645-656.
[4]
Xing J, Wang J D, Mathur R, et al. Impacts of aerosol direct effects on tropospheric ozone through changes in atmospheric dynamics and photolysis rates[J]. Atmospheric Chemistry and Physics, 2017,17(16):9869-9883.
[5]
任宇超,邹北冰,朱乔,等.深圳市近年来PM2.5污染控制效果分析[J]. 环境污染与防治, 2017,39(2):117-121. Ren Y C, Zhou B B, Zhu Q, et al. Effects of control measures on Shenzhen PM2.5 pollution in recent years[J]. Environmental Pollution and Control, 2017,39(2):117-121.
[6]
深圳市人居环境委员会.2016年度深圳市环境状况公报[R]. 深圳:深圳市生态环境局, 2017. Shenzhen Human Settlements and Environment Commission. Environmental status bulletin of Shenzhen in 2016[R]. Shenzhen:Shenzhen Municipal Ecological Environment Bureau, 2017.
[7]
冯凝,唐梦雪,李孟林,等.深圳市城区VOCs对PM2.5和O3耦合生成影响研究[J]. 中国环境科学, 2021,41(1):11-17. Feng N, Tang M X, Li M L, et al. Research on the influence of VOCs on the coupling generation of PM2.5 and O3 in Shenzhen[J]. China Environmental Science, 2021,41(1):11-17.
[8]
叶代启.工业挥发性有机物的排放与控制[M]. 北京:科学出版社, 2017:62-63. Ye D Q. Emission and control of industrial volatile organic compounds[M]. Beijing:Science Press, 2017:62-63.
[9]
徐晨曦,陈军辉,韩丽,等.四川省典型行业挥发性有机物源成分谱[J]. 环境科学, 2020,41(7):3031-3041. Xu C X, Cheng J H, Han L, et al. Source composition spectrum of volatile organic compounds in typical industries in Sichuan[J]. Environmental Science, 2020,41(7):3031-3041.
[10]
齐一谨,倪经纬,赵东旭,等.郑州市典型工业企业VOCs排放特征及风险评估[J]. 环境科学, 2020,41(7):3056-3065. Qi Y J, Ni J W, Zhao D X, et al. Emission characteristics and risk assessment of volatile organic compounds from typical factories in Zhengzhou[J]. Environmental Science, 2020,41(7):3056-3065.
[11]
吕大器,陆思华,谭鑫,等.典型地方炼化企业VOCs排放特征及其对二次污染生成的贡献[J]. 环境科学研究, 2021,34(1):103-113. Lui D Q, Lu S H, Tan X, et al. Emission characteristics of VOCs from typical local refineries and associated contributions to secondary pollution[J]. Research of Environmental Science, 2021,34(1):103-113.
[12]
于广河,朱乔,夏士勇,等.深圳市典型工业行业VOCs排放谱特征研究[J]. 环境科学与技术, 2018,41(S1):232-236. Yu G H, Zhu Q, Xia S Y, et al. Emission characteristics of volatile organic compounds (VOCs) source profile from typical industries in Shenzhen[J]. Environmental Science and Technology, 2018,41(S1):232-236.
[13]
陈雪,黄晓锋,朱波,等.深圳市秋季VOCs空间分布特征与关键减排物种[J]. 中国环境科学, 2021,41(9):4069-4076. Chen X, Huang X F, Zhu B, et al. Spatial distribution characteristics of VOCs pollution and identification of key pollution species in autumn Shenzhen[J]. China Environmental Science, 2021,41(9):4069-4076.
[14]
United States Environmental Protection Agency. Compendium method TO-15 determination of volatile organic compounds (VOCs) in air collected in specially-prepared canisters and analyzed by GC MS[R]. Washington DC:Office of Research and Development, 1999:14-28.
[15]
Zheng J Y, Yu Y F, Mo Z W, et al. Industrial sector-based volatile organic compound (VOC) source profiles measured in manufacturing facilities in the Pearl River Delta, China[J]. Science of the Total Environment, 2013,456-457:127-136.
[16]
邵敏,袁斌,王鸣,等.挥发性有机物(VOCs)来源及其大气化学作用[M]. 北京:科学出版社, 2020:123-125. Shao M, Yuan B, Wang M, et al. Sources of volatile organic compounds (VOCs) and their atmospheric chemical effects[M]. Beijing:Science Press, 2020,123-125.
[17]
Carter W P. SAPRC atmospheric chemical mechanisms and VOC reactivity scales[R]. http://www.engr.ucr.edu/~carter/SAPRC/, 2013.
[18]
Derwent R G, Jenkin M E, Utembe S R, et al. Secondary organic aerosol formation from a large number of reactive man-made organic compounds[J]. Science of the Total Environment, 2010,408(16):3374-3381.
[19]
Zhang Z J, Wang H, Chen D, et al. Emission characteristics of volatile organic compounds and their secondary organic aerosol formation potentials from a petroleum refinery in Pearl River Delta, China[J]. Science of the Total Environment, 2017,1162:584-585.
[20]
Atkinson R, Arey J. Atmospheric degradation of volatile organic compounds[J]. Chemical Reviews, 2003,103(12):4605-4638.
[21]
黄玉虎,胡玮,李贝贝,等.北京城市副中心(通州区)加油站VOCs排放清单[J]. 环境科学, 2018,39(2):618-625. Huang Y H, Hu W, Li B B, et al. VOCs emission inventory of service stations in a subcenter (Tongzhou District) of the City of Beijing[J]. Environmental Science, 2018,39(2):618-625.
[22]
潘洁晨.涂料中VOC的散发与残留研究[D]. 杭州:浙江大学, 2015. Pan J C. Study of the emission and residual of VOC in paint[D]. Hangzhou:Zhejiang University, 2015.
[23]
Liu S L, Wang B G, He J, et al. Source fingerprints of volatile organic compounds emitted from a municipal solid waste incineration power plant in Guangzhou, China[J]. Procedia Environmental Sciences, 2012,12:106-115.
[24]
Setyan A, Patrick M, Wang J. Very low emissions of airborne particulate pollutants measured from two municipal solid waste incineration plants in Switzerland[J]. Atmospheric Environment, 2017,166:99-109.
[25]
翁史烈,罗永浩.大型城市生活垃圾可持续综合利用战略研究[M]. 重庆:重庆出版社, 2016:52-59. Weng S L, Luo Y H. Research on the strategy of sustainable comprehensive utilization of large-scale municipal solid waste[M]. Chongqing:Chongqing Press, 2016:52-59.
[26]
Wang Q L, Li S J, Dong M L, et al. VOCs emission characteristics and priority control analysis based on VOCs emission inventories and ozone formation potentials in Zhoushan[J]. Atmospheric Environment, 2018,182:234-241.
[27]
Shen L J, Xiang P, Liang S W, et al. Sources profiles of volatile organic compounds (VOCs) measured in a typical industrial process in Wuhan, Central China[J]. Atmosphere, 2018,9(8):297.
[28]
段乐君,袁自冰,沙青娥,等.不同排放标准下机动车挥发性有机化合物排放特征趋势研究[J]. 环境科学学报, 2021,41(4):1239-1249. Duan L J, Yuan Z B, Sha Q E, et al. Investigation on the trend of emission characteristics of volatile organic compounds from motor vehicle exhaust under different emission standards[J]. Acta Scientiae Circumstantiae, 2021,41(4):1239-1249.
[29]
Mo Z W, Shao M, Lu S H. Compilation of a source profile database for hydrocarbon and OVOC emissions in China[J]. Atmospheric Environment, 2016,143:209-217.
[30]
陈立军.丙烯酸酯类聚合物乳液的制备及其相关应用的研究[D]. 广州:华南理工大学, 2006. Chen L J. Study on preparation of acrylate polymer emulsions and their related applications[D]. Guangzhou:South China University of Technology, 2006.
[31]
Liang X M, Sun X B, Xu J T, et al. Improved emissions inventory and VOCs speciation for industrial OFP estimation in China[J]. Science of the Total Environment, 2020,745:140838.
[32]
Guan H, Wang X, Han R, et al. High-resolution and-precision spectra of acetonitrile at the V5-band for laser remote sensing[J]. Journal of Quantitative Spectroscopy and Radiative Transfer, 2020,255:107254.
[33]
Huangfu Y B, Yuan B, Wang S H, et al. Revisiting acetonitrile as tracer of biomass burning in anthropogenic-influenced environments[J]. Geophysical Research Letters, 2021,48(11).
[34]
Zhou H, Meng A H, Long Y Q, et al. An overview of characteristics of municipal solid waste fuel in China:Physical, chemical composition and heating value[J]. Renewable and Sustainable Energy Reviews, 2014,36:107-122.
[35]
Jay K, Stieglitz L. Identification and quantification of volatile organic components in emissions of waste incineration plants[J]. Chemosphere, 1995,30(7):1249-1260.
[36]
莫梓伟.挥发性有机物排放源成分谱的构建和评估[D]. 北京:北京大学, 2015. Mo Z W. Compilation and evaluation of VOC source profiles in China[D]. Beijing:Peking University, 2015.
[37]
Chen W T, Shao M, Lu S H, et al. Understanding primary and secondary sources of ambient carbonyl compounds in Beijing using the PMF model[J]. Atmospheric Chemistry and Physics, 2014,14(6):3047-3062.
[38]
景盛翱,王红丽,朱海林,等.典型工业源VOCs治理现状及排放组成特征[J]. 环境科学, 2018,39(7):3090-3095. Jing S A, Wang H L, Zhu M L, et al. Treatment status and emission characteristics of volatile organic compounds from typical industrial sources[J]. Environmental Science, 2018,39(7):3090-3095.