Characteristics and influence factors of PAHs in PM10 and PM2.1 in urban and suburban Nanjing, China
LI Hao1,2, FAN Shu-xian1,2,3, ZHANG Yue2, KANG Bo-shi2, SUN Yu4
1. Collaborative Innovation Center of Atmospheric Environment and Equipment Technology, Nanjing University of Information Science and Technology, Nanjing 210044, China;
2. Nanjing University of Information Science and Technology, Department of Atmospheric Physics, Nanjing 210044, China;
3. Key Laboratory for Aerosol-Cloud-Precipitation of China Meteorological Administration, Nanjing University of Information Science and Technology, Nanjing 210044, China;
4. Meteorology Bureau of Hanjiang District of Yangzhou, Yangzhou 225009, China
PM2.1 and PM10 samples were synchronously collected at suburban and urban sites in Nanjing, 16 kinds of PAHs were analyzed by the GC-MS. The concentrations of total PAHs at the urban and suburban were in the ranges of 32.84~245.35ng/m3 and 21.43~225.72ng/m3 for PM10, respectively, and 19.11~111.57ng/m3 and 19.69~125.21ng/m3 for PM2.1. PAHs concentrations at the two sites were close to each other, and show similar seasonal variation with the winter concentrations larger than those in the summer. PAHs mainly compose of 4-, 5- and 6-ring PAHs that have mass fractions (to total PAH mass) of 78.7%~83.1% in PM10 and 80.5%~87.1% in PM2.1, and the fraction of 4-rings PAHs in winter was clearly larger than those of other seasons. The PAHs at two sites showed different diurnal variations. At the urban site, the concentration in the daytime was higher than that in the nighttime, whereas values in the nighttime become larger at the suburban site. Among the various meteorological parameters, the PAH concentration shows clearly negative correlations to both temperature and relative humidity, and a positive correlation is noticed between the PM10 and PAHs. The influence of meteorological parameters was more significant in warm seasons (summer and autumn) than that in cold seasons (winter and spring). Ozone concentration also had a negative correlation to the 5- and 6-ring PAHs concentration. The results from air mass back-trajectory model show that the accumulation of PAHs was mainly influenced by local emission, and polluted airs from southwest and southeast of Nanjing are also an important source of the PAHs through shout-range transport.
李皓, 樊曙先, 张悦, 康博识, 孙玉. 南京市区郊区大气PM10、PM2.1中PAHs的分布特征及影响因素[J]. 中国环境科学, 2017, 37(1): 60-68.
LI Hao, FAN Shu-xian, ZHANG Yue, KANG Bo-shi, SUN Yu. Characteristics and influence factors of PAHs in PM10 and PM2.1 in urban and suburban Nanjing, China. CHINA ENVIRONMENTAL SCIENCECE, 2017, 37(1): 60-68.
Zhang Y,Tao S.Seasonal variation of polycyclic aromatic hydrocarbons (PAHs) emissions in China[J].Environmental Pollution 156,2008:657-663.
[5]
Liu J,Li J,Lin T,et al.Diurnal and nocturnal variations of PAHs in the Lhasa atmosphere,Tibetan Plateau:Implication for local sources and the impact of atmospheric degradation processing[J].Atmospheric Research,2013,124(5):34-43.
Lai I C,Lee C L,Zeng K Y,et al.Seasonal variation of atmospheric polycyclic aromatic hydrocarbons along the Kaohsiung coast.[J].Journal of Environmental Management,2011,92(8):2029-2037.
[8]
Callén M S,López J M,Mastral A M.Seasonal variation of benzo (a) pyrene in the Spanish airborne PM10.Multivariate linear regression model applied to estimate BaP concentrations[J].Journal of Hazardous Materials,2010,180(1-3):648-655.
[9]
Akyüz M,Çabuk H.Meteorological variations of PM2.5/PM10 concentrations and particle-associated polycyclic aromatic hydrocarbons in the atmospheric environment of Zonguldak,Turkey.[J].Journal of Hazardous Materials,2009,170(1):13-21.
[10]
Niu S J,Liu D Y,Zhao L J,et al.Summary of a 4-Year fog field study in Northern Nanjing,Part 2:Fog microphysics[J].Pure&Applied Geophysics,2012,169(5):1137-1155.
[11]
Niu Shengjie,Lu Chunsong,Yu Huaying,et al.Fog research in China:An overview[J].Advances in Atmospheric Sciences,2010,27(3):639-662.
Meng Qingzi,Fan S,He J,et al.Particle size distribution and characteristics of polycyclic aromatic hydrocarbons during a heavy haze episode in Nanjing,China[J].Particuology,2015,18(1):127-134.
Wang G,Kawamura K,Zhao X,et al.Identification,abundance and seasonal variation of anthropogenic organic aerosols from a mega-city in China[J].Atmospheric Environment,2007,41(2):407-416.
[21]
He J,Fan S,Meng Q,et al.Polycyclic aromatic hydrocarbons (PAHs) associated with fine particulate matters in Nanjing,China:Distributions,sources and meteorological influences[J].Atmospheric Environment,2014,89(2):207-215.
Rogge W F,Hildemann L M,Mazurek M A,et al.Sources of fine organic aerosol.4.Particulate abrasion products from leaf surfaces of urban plants[J].Environmental Science&Technology,1993,27(13):2700-2711.
Kong S,Lu B,Ji Y,et al.Distribution and sources of polycyclic aromatic hydrocarbons in size-differentiated re-suspended dust on building surfaces in an oilfield city,China[J].Atmospheric Environment,2012,55(55):7-16.
Gordana P,Ivana J,Anica Š,et al.Influence of ozone and meteorological parameters on levels of polycyclic aromatic hydrocarbons in the air[J].Atmospheric Environment,2016,131:263-268.
[32]
Amarillo A C,Carreras H.Quantifying the in fluence of meteorological variables on particle-bound PAHs in urban environments[J]Atmospheric Pollution Research,2016,7(4):597-602.