Characteristics and sources of polycyclic aromatic hydrocarbons in atmospheric aerosols in the Kathmandu Valley, Nepal

被引:80
作者
Chen, Pengfei [1 ,5 ]
Kang, Shichang [2 ,3 ,4 ]
Li, Chaoliu [1 ]
Rupakheti, Maheswar
Yan, Fangping [2 ,5 ]
Li, Quanlian [2 ]
Ji, Zhenming [1 ]
Zhang, Qianggong [1 ,3 ,4 ]
Luo, Wei [6 ]
Sillanpaa, Mika [7 ]
机构
[1] Chinese Acad Sci, Inst Tibetan Plateau Res, Key Lab Tibetan Environm Changes & Land Surface P, Beijing 100101, Peoples R China
[2] Chinese Acad Sci, Cold & Arid Reg Environm & Engn Res Inst, State Key Lab Cryospher Sci, Lanzhou 730000, Peoples R China
[3] Chinese Acad Sci, Ctr Excellence Tibetan Plateau Earth Sci, Beijing 100085, Peoples R China
[4] Inst Adv Sustainabil Studies, D-14467 Potsdam, Germany
[5] Chinese Acad Sci, Grad Univ, Beijing 100039, Peoples R China
[6] Chinese Acad Sci, State Key Lab Urban & Reg Ecol, Ecoenvironm Sci Res Ctr, Beijing 100085, Peoples R China
[7] Lappeenranta Univ Technol, Lab Green Chem, Mikkeli 50130, Finland
基金
芬兰科学院; 中国国家自然科学基金;
关键词
Polycyclic aromatic hydrocarbons; Total suspended particles; Source; Health risk; Kathmandu; AIR-POLLUTION; SOURCE IDENTIFICATION; SPATIAL-DISTRIBUTION; NORTH PACIFIC; PAHS; PM10; EMISSIONS; RATIOS; HEALTH; CITY;
D O I
10.1016/j.scitotenv.2015.08.006
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The Kathmandu Valley in the foothills of the Himalayas, where the capital city of Nepal is located, has one of the most serious air pollution problems in the world. In this study, total suspended particle (TSP) samples collected over a year (April 2013-March 2014) in the Kathmandu Valley were analyzed for determining the concentrations of 15 priority particle-bound polycyclic aromatic hydrocarbons (PAHs). The TSP and PAN concentrations were extremely high, with annual average concentration being 199 +/- 124 mu g/m(3) and 155 +/- 130 ng/m(3), respectively, which are comparable to those observed in Asian cities such as Beijing and Delhi. The TSP and PAH concentrations varied considerably, with the seasonal average concentration being maximal during the post-monsoon season followed by, in descending order, the winter, pre-monsoon, and monsoon seasons. In the winter and pre-monsoon seasons, ambient TSP and PAN concentrations increased because of emissions from brick kilns and the use of numerous small generators. Moreover, in the pre-monsoon season, forest fires in the surrounding regions influenced the TSP and PAH concentrations in the valley. PAHs with 4 to 6 rings constituted a predominant proportion (92.3-93.3%) of the total PAHs throughout the year. Evaluation of diagnostic molecular ratios indicated that the atmospheric PAHs in the Kathmandu Valley originated mainly from diesel and biomass combustion. The toxic equivalent quantity (TEQ) of particle phase PAHs ranged between 2.74 and 81.5 ng TEQ/m(3), which is considerably higher than those reported in other South Asian cities, and 2-80 times higher than the World Health Organization guideline (1 ng TEQ/m3). This suggests that ambient PAH levels in the Kathmandu Valley pose a serious health risk to its approximately 3.5 million residents. (C) 2015 Elsevier B.V. All rights reserved.
引用
收藏
页码:86 / 92
页数:7
相关论文
共 56 条
[21]   Atmospheric concentrations, sources and gas-particle partitioning of PAHs in Beijing after the 29th Olympic Games [J].
Ma, Wan-Li ;
Sun, De-Zhi ;
Shen, Wei-Guo ;
Yang, Meng ;
Qi, Hong ;
Liu, Li-Yan ;
Shen, Ji-Min ;
Li, Yi-Fan .
ENVIRONMENTAL POLLUTION, 2011, 159 (07) :1794-1801
[22]   Concentrations, sources, and exposure profiles of polycyclic aromatic hydrocarbons (PAHs) in particulate matter (PM10) in the north central part of India [J].
Masih, Amit ;
Saini, Renuka ;
Singhvi, Raj ;
Taneja, Ajay .
ENVIRONMENTAL MONITORING AND ASSESSMENT, 2010, 163 (1-4) :421-431
[23]  
MEPC, 1996, 309596 MEPC GB
[24]   Black carbon record based on a shallow Himalayan ice core and its climatic implications [J].
Ming, J. ;
Cachier, H. ;
Xiao, C. ;
Qin, D. ;
Kang, S. ;
Hou, S. ;
Xu, J. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2008, 8 (05) :1343-1352
[25]  
NEERI, 2006, AMB QUAL STAT 10 CIT
[26]   City air pollution of polycyclic aromatic hydrocarbons and other mutagens: Occurrence, sources and health effects [J].
Nielsen, T ;
Jorgensen, HE ;
Larsen, JC ;
Poulsen, M .
SCIENCE OF THE TOTAL ENVIRONMENT, 1996, 189 :41-49
[27]   TOXIC EQUIVALENCY FACTORS (TEFS) FOR POLYCYCLIC AROMATIC-HYDROCARBONS (PAHS) [J].
NISBET, ICT ;
LAGOY, PK .
REGULATORY TOXICOLOGY AND PHARMACOLOGY, 1992, 16 (03) :290-300
[28]   Determination of octanol-air partition coefficients and supercooled liquid vapor pressures of PAHs as a function of temperature: Application to gas-particle partitioning in an urban atmosphere [J].
Odabasi, Mustafa ;
Cetin, Eylem ;
Sofuoglu, Aysun .
ATMOSPHERIC ENVIRONMENT, 2006, 40 (34) :6615-6625
[29]   Polycyclic aromatic hydrocarbons (PAHs) in the aerosol in Beijing, China, measured by aminopropylsilane chemically-bonded stationary-phase column chromatography and HPLC/fluorescence detection [J].
Okuda, Tomoaki ;
Naoi, Daisuke ;
Tenmoku, Masaki ;
Tanaka, Shigeru ;
He, Kebin ;
Ma, Yongliang ;
Yang, Fumo ;
Lei, Yu ;
Jia, Yingtao ;
Zhang, Dihan .
CHEMOSPHERE, 2006, 65 (03) :427-435
[30]   Diurnal cycle of air pollution in the Kathmandu Valley, Nepal: Observations [J].
Panday, Arnico K. ;
Prinn, Ronald G. .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2009, 114 :D09305