|
|
Vertical distribution monitoring of near-surface atmospheric VOCs in Shenzhen based on UAV-borne |
WANG Bi1, CHENG Yong1, YU Guang-he2, LI Xin2, WANG Hai-chao3, ZHENG Ze-long3, ZENG Li-wu1, HUANG Xiao-feng1 |
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. Guangdong Laboratory of Southern Marine Science and Engineering, School of Atmospheric Sciences, Sun Yat-sen University, Zhuhai 519082, China |
|
|
Abstract From September 21 to 23, 2023, a study was conducted in Shenzhen using a multi-channel airborne sampling system on unmanned aerial vehicle (UAV) equipped with in-house NO2 and O3 integrated monitoring devices in seven gradient levels during morning and afternoon periods. This study aimed to investigate the vertical distribution characteristics, composition evolution, and their impact on ozone formation of volatile organic compounds (VOCs) from the surface to 480 meters. The results indicated that the concentrations of VOCs in the morning decreased with height, reflecting a significant influence of ground emissions, while it increased with height in the afternoon, influencing by regional transport. The main VOC species were OVOCs and alkanes, with their concentrations peaking at 160~240meters and 400meters due to emission sources, while other species exhibited minor fluctuations. The vertical distribution characteristics of the total ozone formation potential (OFP) were consistent with the total VOCs concentration. The major contributors to OFP were OVOCs (36.9%), olefins (25.2%), and aromatics (22.4%). Ratio analysis of typical and characteristic species suggested that secondary production, industrial processes, solvent usage sources, and vehicular emissions have a significant impact on the vertical distribution of VOCs. Furthermore, during the observation period, the NO2 concentration increased with altitude above 240 meters in morning and noon. The O3 concentration peaked at 160 meters during the morning, and showed an opposite trend to NO2 above 240 meters during the afternoon, influenced by the synergistic effects of VOCs and NO2.
|
Received: 27 October 2023
|
|
|
|
|
[1] Li K, Li J, Tong S, et al. Characteristics of wintertime VOCs in suburban and urban Beijing:Concentrations, emission ratios, and festival effects[J]. Atmos Chem Phys, 2019,19(12):8021-8036. [2] Li L, Lu C, Chan P W, et al. Tower observed vertical distribution of PM2.5, O3 and NOx in the Pearl River Delta[J]. Atmospheric Environment, 2020,220:117083. [3] Bari M A, Kindzierski W B. Ambient volatile organic compounds (VOCs) in Calgary, Alberta:Sources and screening health risk assessment[J]. Science of The Total Environment, 2018,631-632:627-640. [4] Liu Y, Song M, Liu X, et al. Characterization and sources of volatile organic compounds (VOCs) and their related changes during ozone pollution days in 2016 in Beijing, China[J]. Environmental Pollution, 2020,257:113599. [5] Han M, Lu X, Zhao C, et al. Characterization and source apportionment of volatile organic compounds in urban and suburban Tianjin, China[J]. Advances in Atmospheric Sciences, 2015,32(3):439-444. [6] Li B, Ho S S H, Li X, et al. Pioneering observation of atmospheric volatile organic compounds in Hangzhou in eastern China and implications for upcoming 2022 Asian Games[J]. Journal of Environmental Sciences, 2023,124:723-734. [7] Mo Z, Shao M, Lu S, et al. Characterization of non-methane hydrocarbons and their sources in an industrialized coastal city, Yangtze River Delta, China[J]. Science of The Total Environment, 2017,593-594:641-653. [8] Guo H, Ling Z H, Cheng H R, et al. Tropospheric volatile organic compounds in China[J]. Science of The Total Environment, 2017, 574:1021-1043. [9] Sun J, Wang Y, Wu F, et al. Vertical characteristics of VOCs in the lower troposphere over the North China Plain during pollution periods[J]. Environmental Pollution, 2018,236:907-915. [10] Mo Z, Shao M, Wang W, et al. Evaluation of biogenic isoprene emissions and their contribution to ozone formation by ground-based measurements in Beijing, China[J]. Science of The Total Environment, 2018,627:1485-1494. [11] Xue L, Wang T, Simpson I J, et al. Vertical distributions of non-methane hydrocarbons and halocarbons in the lower troposphere over northeast China[J]. Atmospheric Environment, 2011,45(36):6501-6509. [12] Zhang K, Xiu G, Zhou L, et al. Vertical distribution of volatile organic compounds within the lower troposphere in late spring of Shanghai[J]. Atmospheric Environment, 2018,186:150-157. [13] Sun C H, Zhao L, Chen X L, et al. A comprehensive study of volatile organic compounds from the actual emission of Chinese cooking[J]. Environmental Science and Pollution Research, 2021,29:53821-53830. [14] Silva J, Rojas Quincho J, Norabuena M, et al. Ozone and volatile organic compounds in the metropolitan area of Lima-Callao, Peru[J]. Air Quality, Atmosphere&Health, 2018,11. [15] Hien V, Lin C, Vu C T, et al. An overview of the development of vertical sampling technologies for ambient volatile organic compounds (VOCs)[J]. Journal of Environmental Management, 2019,247:401-412. [16] Yang S, Li X, Zeng L, et al. Development of multi-channel whole-air sampling equipment onboard an unmanned aerial vehicle for investigating volatile organic compounds'vertical distribution in the planetary boundary layer[J]. Atmos Meas Tech, 2023,16(2):501-512. [17] Mo Z, Huang S, Yuan B, et al. Deriving emission fluxes of volatile organic compounds from tower observation in the Pearl River Delta, China[J]. Science of The Total Environment, 2020,741:139763. [18] 崔卓彦,邱志诚,孙天乐,等.深圳近地层大气日间VOCs垂直分布特征观测研究[J].环境科学学报, 2023,43(8):226-234. Cui Z Y, Qiu Z C, Sun T L et al. Study on the vertical distribution characteristics of VOCs in the near-ground atmosphere during daytime in Shenzhen[J]. Chinese Journal of Environmental Sciences, 2019,43(8):226-234. [19] Kaser L, Peron A, Graus M, et al. Interannual variability of terpenoid emissions in an alpine city[J]. Atmospheric Chemistry and Physics, 2022,22:5603-5618. [20] Permar W, Wang Q, Selimovic V, et al. Emissions of Trace Organic Gases From Western U.S. Wildfires Based on WE-CAN Aircraft Measurements[J]. Journal of Geophysical Research:Atmospheres, 2021,126. [21] Wu S, Tang G, Wang Y, et al. Vertically decreased VOC concentration and reactivity in the planetary boundary layer in winter over the North China Plain[J]. Atmospheric Research, 2020,240:104930. [22] Mckinney K, Wang D, Ye J, et al. A sampler for atmospheric volatile organic compounds by copter unmanned aerial vehicles[J]. Atmospheric Measurement Techniques, 2019,12:3123-3135. [23] Yu F, Liu Y, Fan L, et al. Design and implementation of atmospheric multi-parameter sensor for UAV-based aerosol distribution detection[J]. Sensor Review, 2017,37:196-210. [24] 廖彤,张涛,周炎,等.珠三角典型地区大气污染时段VOCs特征及化学反应活性[J].环境科学学报, 2023,43(1):229-236. Liao T, Zhang T, Zhou Y, et al. VOCs characteristics and chemical reactivity in typical air pollution periods in the Pearl River Delta[J]. Journal of Environmental Sciences, 2019,43(1):229-236. [25] Zhu B, Huang X, Xia S, et al. Biomass-burning emissions could significantly enhance the atmospheric oxidizing capacity in continental air pollution[J]. Environmental Pollution, 2021,285:117523. [26] Shi Y, Ren J, Xi Z, et al. Identification of key anthropogenic VOC species and sources controlling summer ozone formation in China[J]. Atmospheric Environment, 2023,298:119623. [27] Chen G J, Shi Q, Xu L L, et al. Photochemistry in the urban agglomeration along the coastline of southeastern China:Pollution mechanism and control implication[J]. Science of The Total Environment, 2023,901. [28] 郑品梅,孙天乐,朱波,等.基于铁塔观测的深圳大气VOCs垂直分布特征[J].中国环境科学, 2023,43(1):29-37. Zheng P M, Sun T L, Zhu B, et al. Vertical distribution characteristics of atmospheric VOCs in Shenzhen based on observation of iron towers[J]. China Environmental Science, 2023,43(1):29-37. [29] Mo Z, Huang S, Yuan B, et al. Tower-based measurements of NMHCs and OVOCs in the Pearl River Delta:Vertical distribution, source analysis and chemical reactivity[J]. Environmental Pollution, 2021, 292:118454. [30] 范绍佳,王海潮,卢骁,等.20世纪90年代以来粤港澳大湾区臭氧污染研究进展[J].环境科学学报, 2023,43(1):1-18. Fan S J, Wang H C, Lu X, et al. Research progress on ozone pollution in the Guangdong-Hong Kong-Macao Greater Bay Area since 1990s[J]. China Environmental Science, 2023,43(1):1-18. [31] Yu D, Tan Z F, Lu K D, et al. An explicit study of local ozone budget and NOx-VOCs sensitivity in Shenzhen China[J]. Atmospheric Environment, 2020,224. [32] He Z, Wang X, Ling Z, et al. Contributions of different anthropogenic volatile organic compound sources to ozone formation at a receptor site in the Pearl River Delta region and its policy implications[J]. Atmospheric Chemistry and Physics, 2019,19:8801-8816. [33] Carter W P L. Development of a condensed SAPRC-07chemical mechanism[J]. Atmospheric Environment, 2010,44(40):5336-5345. [34] Atkinson R, Arey J. Atmospheric Degradation of Volatile Organic Compounds[J]. Chemical Reviews, 2003,103(12):4605-4638. [35] Cliff S J, Lewis A C, Shaw M D, et al. Unreported VOC Emissions from Road Transport Including from Electric Vehicles[J]. Environmental Science&Technology, 2023,57(21):8026-8034. [36] 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&Technology, 2018,41(S1):232-236. [37] 黄沛荣,朱波,张月,等.PM2.5与O3协同控制视角下深圳市工业VOCs源谱特征[J].中国环境科学, 2022,42(8):3473-3482. Huang P R, Zhu B, Zhang Y, et al. Source profile characteristics of industrial VOCs in Shenzhen from the perspective of PM2.5 and O3 synergistic control[J]. China Environmental Science, 2022,42(8):3473-3482. [38] Zhang J, Zhu X, Tao S, et al. Mixing layer height and its implications for air pollution in Beijing, China[J]. Atmospheric Chemistry and Physics, 2016,16:2459-2475. [39] Hui L, Liu X, Tan Q, et al. VOC characteristics, chemical reactivity and sources in urban Wuhan, central China[J]. Atmospheric Environment, 2020,224:117340. [40] Hui L, Liu X, Tan Q, et al. Characteristics, source apportionment and contribution of VOCs to ozone formation in Wuhan, Central China[J]. Atmospheric Environment, 2018,192:55-71. [41] Barletta B, Meinardi S, Simpson I, et al. Ambient mixing ratios of nonmethane hydrocarbons (NMHCs) in two major urban centers of the Pearl River Delta (PRD) region:Guangzhou and Dongguan[J]. Atmospheric Environment-ATMOS ENVIRON, 2008,42:4393-4408. [42] Kumar A, Singh D, Kumar K, et al. Distribution of VOCs in urban and rural atmospheres of subtropical India:Temporal variation, source attribution, ratios, OFP and risk assessment[J]. The Science of the total environment, 2017,613-614:492-501. [43] Yurdakul S, Civan M, KuntasalÖ, et al. Temporal variations of VOC concentrations in Bursa atmosphere[J]. Atmospheric Pollution Research, 2018,9(2):189-206. [44] Zhang Z, Zhang Y, Wang X, et al. Spatiotemporal patterns and source implications of aromatic hydrocarbons at six rural sites across China's developed coastal regions[J]. Journal of Geophysical Research:Atmospheres, 2016,121:6669-6687. [45] 罗达通,张青梅,刘湛,等.长株潭城区8月VOCs污染特征及来源分析[J].环境科学, 2022,43(7):3463-3472. Luo D T, Zhang Q M, Liu Z, et al. Characteristics and source apportionment of volatile organic compounds in August, Chang-Zhu-Tan urban area[J]. Environmental Science, 2022,43(7):3463-3472. [46] Lai C H, Chang C C, Wang C H, et al. Emissions of liquefied petroleum gas (LPG) from motor vehicles[J]. Atmospheric Environment, 2009,43:1456-1463. [47] Huang A, Yin S, Yuan M, et al. Characteristics, source analysis and chemical reactivity of ambient VOCs in a heavily polluted city of central China[J]. Atmospheric Pollution Research, 2022,13(4):101390. [48] Liu B, Liang D, Yang J, et al. Characterization and source apportionment of volatile organic compounds based on 1-year of observational data in Tianjin, China[J]. Environmental Pollution, 2016, 218:757-769. |
|
|
|