CLC number: TV5
On-line Access: 2024-08-27
Received: 2023-10-17
Revision Accepted: 2024-05-08
Crosschecked: 2017-12-15
Cited: 1
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Ling-hong Chen, Biao Lv, Xian-jue Zheng, Kang-wei Li, Jian-dong Shen, Kai-ji Bao, Xue-cheng Wu, Cheng-hang Zheng, Fang Ying, Xiang Gao, Ke-fa Cen. Effect of relative humidity on non-refractory submicron aerosol evolution during summertime in Hangzhou, China[J]. Journal of Zhejiang University Science A, 2018, 19(1): 45-59.
@article{title="Effect of relative humidity on non-refractory submicron aerosol evolution during summertime in Hangzhou, China",
author="Ling-hong Chen, Biao Lv, Xian-jue Zheng, Kang-wei Li, Jian-dong Shen, Kai-ji Bao, Xue-cheng Wu, Cheng-hang Zheng, Fang Ying, Xiang Gao, Ke-fa Cen",
journal="Journal of Zhejiang University Science A",
volume="19",
number="1",
pages="45-59",
year="2018",
publisher="Zhejiang University Press & Springer",
doi="10.1631/jzus.A1700567"
}
%0 Journal Article
%T Effect of relative humidity on non-refractory submicron aerosol evolution during summertime in Hangzhou, China
%A Ling-hong Chen
%A Biao Lv
%A Xian-jue Zheng
%A Kang-wei Li
%A Jian-dong Shen
%A Kai-ji Bao
%A Xue-cheng Wu
%A Cheng-hang Zheng
%A Fang Ying
%A Xiang Gao
%A Ke-fa Cen
%J Journal of Zhejiang University SCIENCE A
%V 19
%N 1
%P 45-59
%@ 1673-565X
%D 2018
%I Zhejiang University Press & Springer
%DOI 10.1631/jzus.A1700567
TY - JOUR
T1 - Effect of relative humidity on non-refractory submicron aerosol evolution during summertime in Hangzhou, China
A1 - Ling-hong Chen
A1 - Biao Lv
A1 - Xian-jue Zheng
A1 - Kang-wei Li
A1 - Jian-dong Shen
A1 - Kai-ji Bao
A1 - Xue-cheng Wu
A1 - Cheng-hang Zheng
A1 - Fang Ying
A1 - Xiang Gao
A1 - Ke-fa Cen
J0 - Journal of Zhejiang University Science A
VL - 19
IS - 1
SP - 45
EP - 59
%@ 1673-565X
Y1 - 2018
PB - Zhejiang University Press & Springer
ER -
DOI - 10.1631/jzus.A1700567
Abstract: relative humidity (RH) has a significant and complex effect on aerosols because of the aqueous phase process and gas-particle partition. The mass concentration and size distribution of organic aerosols, sulfate, nitrate, ammonium, and chloride were measured using high-resolution time-of-flight aerosol mass spectrometry (HR-ToF-AMS). These measurements were recorded from Aug. 5 to Sept. 23, 2016 in Binjiang District, Hangzhou, China, during which period more than 78% of the readings showed an RH over 60%, while the average temperature was 26 °C. Correlation analysis was applied to inorganic aerosol measurements while positive matrix factorization (PMF) was applied for source apportionment of organic aerosols (OA). The pattern of fixation of ammonium in aerosols changed as the RH increased, suggesting that RH enhances nitrate participation in particles, while sulfate is scavenged by droplets. All species of non-refractory submicron particles (NR-PM1) showed an increase in their peak size as the RH increased. Primary OA (POA) continuously accumulated as the RH increased. When RH<60%, oxygenated OA (OOA) increased with increasing RH because of oxidation; semi-volatile OOA (SV-OOA) had a higher mass concentration during the daytime than at nighttime, indicating that the aqueous phase process and photochemistry synergistically affect the formation of oxygenated SV-OOA. When RH>60%, there was a relatively slow decrease in OOA, dominated by the wet removal effect rather than oxidation. The degree of oxidation of OA decreased as RH increased; this can be explained by most of the OOA with higher hygroscopicity being removed as droplets.
[1]Aiken AC, Salcedo D, Cubison MJ, et al., 2009. Mexico City aerosol analysis during MILAGRO using high resolution aerosol mass spectrometry at the urban supersite (T0)— Part 1: fine particle composition and organic source apportionment. Atmospheric Chemistry & Physics, 9(17):6633-6653.
[2]Aiken AC, Foy BD, Wiedinmyer C, et al., 2010. Mexico City aerosol analysis during MILAGRO using high resolution aerosol mass spectrometry at the urban supersite (T0)— Part 2: analysis of the biomass burning contribution and the modern carbon fraction. Atmospheric Chemistry & Physics, 10(12):5315-5341.
[3]Alfarra MR, Prevot AS, Szidat S, et al., 2007. Identification of the mass spectral signature of organic aerosols from wood burning emissions. Environmental Science & Technology, 41(16):5770-5777.
[4]Canagaratna MR, Jayne JT, Jimenez JL, et al., 2007. Chemical and microphysical characterization of ambient aerosols with the aerodyne aerosol mass spectrometer. Mass Spectrometry Reviews, 26(2):185-222.
[5]Chakraborty A, Gupta T, Tripathi SN, 2016. Combined effects of organic aerosol loading and fog processing on organic aerosols oxidation, composition, and evolution. Science of the Total Environment, 573:690-698.
[6]Collett JL, Herckes P, Youngster S, et al., 2008. Processing of atmospheric organic matter by California radiation fogs. Atmospheric Research, 87(3-4):232-241.
[7]Davidson CI, Phalen RF, Solomon PA, 2005. Airborne particulate matter and human health: a review. Aerosol Science and Technology, 39(8):737-749.
[8]Day DE, Malm WC, 2001. Aerosol light scattering measurements as a function of relative humidity: a comparison between measurements made at three different sites. Atmospheric Environment, 35(30):5169-5176.
[9]Decarlo PF, 2008. Fast airborne aerosol size and chemistry measurements above Mexico City and Central Mexico during the MILAGRO campaign. Atmospheric Chemistry and Physics, 8(14):4027-4048.
[10]Decarlo PF, Slowik JG, Worsnop DR, et al., 2004. Particle morphology and density characterization by combined mobility and aerodynamic diameter measurements. Part 1: theory. Aerosol Science & Technology, 38(12):1185-1205.
[11]Decarlo PF, Kimmel JR, Trimborn A, et al., 2006. Field-deployable, high-resolution, time-of-flight aerosol mass spectrometer. Analytical Chemistry, 78(24):8281-8289.
[12]Ervens B, Turpin BJ, Weber RJ, 2011. Secondary organic aerosol formation in cloud droplets and aqueous particles (aqSOA): a review of laboratory, field and model studies. Atmospheric Chemistry & Physics, 11(8):11(21), 11069-11102.
[13]Fu Q, Zhuang G, Wang J, et al., 2008. Mechanism of formation of the heaviest pollution episode ever recorded in the Yangtze River Delta, China. Atmospheric Environment, 42(9):2023-2036.
[14]Gao S, Ng NL, Keywood M, et al., 2004. Particle phase acidity and oligomer formation in secondary organic aerosol. Environmental Science & Technology, 38(24):6582-6589.
[15]Ge X, Zhang Q, Sun Y, et al., 2012. Effect of aqueous-phase processing on aerosol chemistry and size distributions in Fresno, California, during wintertime. Environmental Chemistry, 9(3):221-235.
[16]Gilardoni S, Massoli P, Giulianelli L, et al., 2014. Fog scavenging of organic and inorganic aerosol in the Po Valley. Atmospheric Chemistry & Physics, 14(13):6967-6981.
[17]Hallquist M, Wenger JC, Baltensperger U, et al., 2009. The formation, properties and impact of secondary organic aerosol: current and emerging issues. Atmospheric Chemistry and Physics, 9(14):5155-5236.
[18]He K, Zhao Q, Ma Y, et al., 2012. Spatial and seasonal variability of PM2.5 acidity at two Chinese megacities: insights into the formation of secondary inorganic aerosols. Atmospheric Chemistry & Physics, 12(3):1377-1395.
[19]He LY, Lin Y, Huang XF, et al., 2010. Characterization of high-resolution aerosol mass spectra of primary organic aerosol emissions from Chinese cooking and biomass burning. Atmospheric Chemistry & Physics, 10(23):11535-11543.
[20]Heald CL, Kroll JH, Jimenez JL, et al., 2010. A simplified description of the evolution of organic aerosol composition in the atmosphere. Geophysical Research Letters, 37(8):162-169.
[21]Hennigan CJ, Bergin MH, Russell AG, et al., 2009. Gas/ Particle partitioning of water-soluble organic aerosol in Atlanta. Atmospheric Chemistry & Physics Discussions, 9(11):3613-3628.
[22]Huang X, Qiu R, Chan CK, et al., 2011. Evidence of high PM2.5 strong acidity in ammonia-rich atmosphere of Guangzhou, China: transition in pathways of ambient ammonia to form aerosol ammonium at [NH4+]/[SO42−] =1.5. Atmospheric Research, 99(3-4):488-495.
[23]Jayne JT, Worsnop DR, Kolb CE, et al., 2000. Development of an aerosol mass spectrometer for size and composition analysis of submicron particles. Aerosol Science & Technology, 33(1-2):49-70.
[24]Jimenez JL, Canagaratna MR, Donahue NM, et al., 2009. Evolution of organic aerosols in the atmosphere. Science, 326(5959):1525-1529.
[25]Kanakidou M, Seinfeld JH, Pandis SN, et al., 2005. Organic aerosol and global climate modelling: a review. Atmospheric Chemistry and Physics, 5(4):1053-1123.
[26]Kaul DS, Gupta T, Tripathi SN, et al., 2011. Secondary organic aerosol: a comparison between foggy and nonfoggy days. Environmental Science & Technology, 45(17):7307-7313.
[27]Kroll JH, Donahue NM, Jimenez JL, et al., 2011. Carbon oxidation state as a metric for describing the chemistry of atmospheric organic aerosol. Nature Chemistry, 3(2):133-139.
[28]Lanz VA, Alfarra MR, Baltensperger U, et al., 2007. Source apportionment of submicron organic aerosols at an urban site by linear unmixing of aerosol mass spectra. Atmospheric Chemistry & Physics, 6(6):11681-11725.
[29]Lim YB, Tan Y, Perri MJ, et al., 2010. Aqueous chemistry and its role in secondary organic aerosol (SOA) formation. Atmospheric Chemistry & Physics Discussions, 10(21):10521-10539.
[30]Matthew BM, Middlebrook AM, Timothy BO, 2008. Collection efficiencies in an aerodyne aerosol mass spectrometer as a function of particle phase for laboratory generated aerosols. Aerosol Science & Technology, 42(11):884-898.
[31]Middlebrook AM, Bahreini R, Jimenez JL, et al., 2012. Evaluation of composition-dependent collection efficiencies for the aerodyne aerosol mass spectrometer using field data. Aerosol Science & Technology, 46(3):258-271.
[32]Middleton P, Kiang CS, Mohnen VA, 1980. Theoretical estimates of the relative importance of various urban sulfate aerosol production mechanisms. Atmospheric Environment, 14(4):463-472.
[33]Mohr C, Huffman A, Cubison MJ, et al., 2009. Characterization of primary organic aerosol emissions from meat cooking, trash burning, and motor vehicles with high-resolution aerosol mass spectrometry and comparison with ambient and chamber observations. Environmental Science & Technology, 43(7):2443-2449.
[34]Ng NL, Canagaratna MR, Zhang Q, et al., 2010. Organic aerosol components observed in Northern Hemispheric datasets from Aerosol Mass Spectrometry. Atmospheric Chemistry and Physics, 10(10):4625-4641.
[35]Ng NL, Canagaratna MR, Jimenez JL, et al., 2011a. Changes in organic aerosol composition with aging inferred from aerosol mass spectra. Atmospheric Chemistry & Physics, 11(13):6465-6474.
[36]Ng NL, Canagaratna MR, Jimenez JL, et al., 2011b. Real-time methods for estimating organic component mass concentrations from aerosol mass spectrometer data. Environmental Science & Technology, 45(3):910-916.
[37]Ortega AM, Hayes PL, Peng Z, et al., 2016. Real-time measurements of secondary organic aerosol formation and aging from ambient air in an oxidation flow reactor in the Los Angeles area. Atmospheric Chemistry & Physics, 16(11):7411-7433.
[38]Paatero P, Tapper U, 1994. Positive matrix factorization: a non-negative factor model with optimal utilization of error estimates of data values. Environmetrics, 5(2):111-126.
[39]Pathak RK, Louie PKK, Chan CK, 2004. Characteristics of aerosol acidity in Hong Kong. Atmospheric Environment, 38(19):2965-2974.
[40]Pathak RK, Wu WS, Wang T, 2009. Summertime PM2.5 ionic species in four major cities of China: nitrate formation in an ammonia-deficient atmosphere. Atmospheric Chemistry and Physics, 9(5):1711-1722.
[41]Saxena P, Seigneur C, 1987. On the oxidation of SO2 to sulfate in atmospheric aerosols. Atmospheric Environment, 21(4):807-812.
[42]Schneider J, Weimer S, Drewnick F, et al., 2006. Mass spectrometric analysis and aerodynamic properties of various types of combustion-related aerosol particles. International Journal of Mass Spectrometry, 258(1-3):37-49.
[43]Seigneur C, Saxena P, 1988. A theoretical investigation of sulfate formation in clouds. Atmospheric Environment, 22(1):101-115.
[44]Seinfeld JH, Pandis SN, 2012. Atmospheric Chemistry and Physics: from Air Pollution to Climate Change, 2nd Edition. John Wiley & Sons, USA.
[45]Seinfeld JH, Erdakos GB, Asher WE, et al., 2001. Modeling the formation of secondary organic aerosol (SOA). 2. The predicted effects of relative humidity on aerosol formation in the alpha-pinene-, beta-pinene-, sabinene-, delta 3-carene-, and cyclohexene-ozone systems. Environmental Science & Technology, 35(9):1806-1817.
[46]Shen X, Lee T, Guo J, et al., 2012. Aqueous phase sulfate production in clouds in eastern China. Atmospheric Environment, 62(15):502-511.
[47]Solomon S, 2007. Climate Change 2007-the Physical Science Basis: Working Group I Contribution to the Fourth Assessment Report of the IPCC (Vol. 4). Cambridge University Press, UK.
[48]Squizzato S, Masiol M, Brunelli A, et al., 2013. Factors determining the formation of secondary inorganic aerosol: a case study in the Po Valley (Italy). Atmospheric Chemistry and Physics, 13(4):1927-1939.
[49]Sun Y, Zhuang G, Tang AA, et al., 2006. Chemical characteristics of PM2.5 and PM10 in haze-fog episodes in Beijing. Environmental Science & Technology, 40(10):3148-3155.
[50]Sun Y, Wang Z, Fu P, et al., 2013. The impact of relative humidity on aerosol composition and evolution processes during wintertime in Beijing, China. Atmospheric Environment, 77(3):927-934.
[51]Tkacik DS, Lambe AT, Jathar S, et al., 2014. Secondary organic aerosol formation from in-use motor vehicle emissions using a potential aerosol mass reactor. Environmental Science & Technology, 48(19):11235-11242.
[52]Tong Z, Whitlow TH, Landers A, et al., 2015. A case study of air quality above an urban roof top vegetable farm. Environmental Pollution, 208(Part A):256-260.
[53]Tong Z, Chen Y, Malkawi A, et al., 2016a. Energy saving potential of natural ventilation in China: the impact of ambient air pollution. Applied Energy, 179(1):660-668.
[54]Tong Z, Chen Y, Malkawi A, 2016b. Defining the Influence Region in neighborhood-scale CFD simulations for natural ventilation design. Applied Energy, 182:625-633.
[55]Tong Z, Yang B, Hopke PK, et al., 2017. Microenvironmental air quality impact of a commercial-scale biomass heating system. Environmental Pollution, 220(Part B):1112-1120.
[56]Ulbrich IM, Canagaratna MR, Zhang Q, et al., 2008. Interpretation of organic components from positive matrix factorization of aerosol mass spectrometric data. Atmospheric Chemistry & Physics, 8(2):2891-2918.
[57]Wong JPS, Lee AKY, Slowik JG, et al., 2011. Oxidation of ambient biogenic secondary organic aerosol by hydroxyl radicals: effects on cloud condensation nuclei activity. Geophysical Research Letters, 38(22):178-181.
[58]Zhang Q, Jimenez JL, Worsnop DR, et al., 2007a. A case study of urban particle acidity and its influence on secondary organic aerosol. Environmental Science & Technology, 41(9):3213-3219.
[59]Zhang Q, Jimenez JL, Canagaratna MR, et al., 2007b. Ubiquity and dominance of oxygenated species in organic aerosols in anthropogenically-influenced Northern Hemisphere midlatitudes. Geophysical Research Letters, 34(13):L13801.
[60]Zhang Q, Jimenez JL, Canagaratna MR, et al., 2011. Understanding atmospheric organic aerosols via factor analysis of aerosol mass spectrometry: a review. Analytical & Bioanalytical Chemistry, 401(10):3045-3067.
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