收稿日期: 2013-08-14
修回日期: 2013-10-25
网络出版日期: 2014-05-15
基金资助
国家环境保护公益性行业科研专项(201009001)资助
Characteristics of hazardous trace elements in PM2.5 in urban area of Chengdu
Received date: 2013-08-14
Revised date: 2013-10-25
Online published: 2014-05-15
在2011年各典型季节月,采集成都城区的PM2.5样品,采用电感耦合等离子体质谱仪(ICP-MS)分析获取32种元素浓度,对其中9种有害元素浓度、富集程度及可能来源进行分析.结果表明,有害元素Pb、Mn、As、Cr、Sb、Cd、Se、Ni和Co的年均浓度分别为(171.7±86.2)、(66.4±36.7)、(19.8±11.1)、(9.2±5.0)、(6.5±4.2)、(3.5±1.9)、(2.7±1.2)、(2.5±1.6)和(0.5±0.3)ng·m-3.绝大多数样品中As浓度超过世界卫生组织和中国环境空气质量标准的参考限值.元素Se、Cd、Sb、Pb和As有明显的富集现象,富集因子均值范围在492~5340.受土壤尘的影响,所有元素的富集因子在春季较低.因子分析结果进一步表明PM2.5中有害微量元素主要来自机动车、燃煤以及金属冶炼等人为来源.
张智胜 , 陶俊 , 龙颖贤 , 林泽健 . 成都城区PM2.5中有害微量元素的污染特征[J]. 中国科学院大学学报, 2014 , 31(3) : 426 -430 . DOI: 10.7523/j.issn.2095-6134.2014.03.019
Daily PM2.5 samples were collected during the typical month of each season of 2011 at an urban site of Chengdu. 32 elements were detected in PM2.5 by ICP-MS, among which there were 9 hazardous elements. The concentrations, enrichment factors, and possible sources of the 9 elements were analyzed in this study. The annual average concentrations of Pb,Mn,As,Cr,Sb,Cd,Se,Ni, and Co were (171.7±86.2), (66.4±36.7), (19.8±11.1), (9.2±5.0), (6.5±4.2), (3.5±1.9), (2.7±1.2), (2.5±1.6), and (0.5±0.3) ng·m-3, respectively. The As concentrations in most of the collected samples exceeded the guideline values provided by WHO and Chinese ambient air quality standards. High enrichment factors of Se,Cd,Sb,Pb, and As were found, ranging from 492 to 5340. Relatively low enrichment factors were observed for all the hazardous elements during spring, since the ambient aerosol was significantly affected by soil dust. The results of the factor analysis further revealed that these hazardous elements were mainly contributed by anthropogenic sources such as motor vehicle emissions, coal combustion, and metal smelting.
Key words: PM2.5; hazardous trace elements; heavy metals; Chengdu
[1] Chan C K, Yao X. Air pollution in mega cities in China[J]. Atmospheric Environment, 2008, 42(1):1-42.
[2] Wu D, Liu F H, Liang Y G, et al. Hazy weather formation and visibility deterioration resulted from fine particulate (PM2.5) pollutions in Guangdong and Hong Kong[J]. Acta Scientiae Circustantiae, 2012, 32(11):2660-2669 (in Chinese). 吴兑, 刘放汉, 梁延刚, 等. 粤港细粒子(PM2.5)污染导致能见度下降与灰霾天气形成的研究[J]. 环境科学学报, 2012, 32(011), 2660-2669.
[3] Jrup L. Hazards of heavy metal contamination[J]. British medical bulletin, 2003, 68(1):167-182.
[4] Pope III C A, Dockery D W. Health effects of fine particulate air pollution: lines that connect[J]. Journal of the Air & Waste Management Association, 2006, 56(6):709-742.
[5] Kampa M, Castanas E. Human health effects of air pollution[J]. Environmental Pollution, 2008, 151(2), 362-367.
[6] USEPA. About Air Toxic..http://www.epa.gov/ttn/atw/allabout.html.
[7] World Health Organization. Air quality guidelines for Europe[M]. 2nd ed. Copenhagen:WHO Regional Publication,2000.
[8] 中华人民共和国环境保护部. 环境空气质量标准 (GB3095—2012)[S].北京:中国环境科学出版社, 2012.
[9] Tan J H, Duan J C. Heavy metals in aerosol in China: pollution, sources, and control strategies[J]. Journal of Graduate University of Chinese Academy of Sciences, 2013, 30(2):145-155 (in Chinese). 谭吉华, 段菁春. 中国大气颗粒物重金属污染, 来源及控制建议[J]. 中国科学院研究生院学报, 2013, 30(2):145-155.
[10] Tao J, Zhang L M, Engling G, et al. Chemical composition of PM2.5 in an urban environment in Chengdu, China: importance of springtime dust storms and biomass burning[J]. Atmospheric Research, 2013, 122:270-283.
[11] Hsu S C, Liu S C, Huang Y T, et al. A criterion for identifying Asian dust events based on Al concentration data collected from northern Taiwan between 2002 and early 2007[J]. Journal of geophysical research, 2008, 113(D18), D18306.
[12] Tao J, Zhang R J, Duan J C, et al. Seasonal variation of carcinogenic heavy metals in PM2.5 and source analysis in Beijing[J]. Environmtal Sciences, 2014,35(2):411-417(in Chinese). 陶俊, 张仁健, 段菁春, 等. 北京城区PM2.5中致癌重金属季节变化特征及其来源分析[J]. 环境科学, 2014, 35(2):411-417.
[13] Chen J, Tan M, Li Y, et al. Characteristics of trace elements and lead isotope ratios in PM2.5 from four sites in Shanghai[J]. Journal of Hazardous Materials, 2008, 156(1):36-43.
[14] Han B, Kong S, Bai Z, et al. Characterization of elemental species in PM2.5 samples collected in four cities of northeast China[J]. Water, Air, & Soil Pollution, 2010, 209(1-4):15-28.
[15] Ho K, Cao J, Lee S, et al. Source apportionment of PM2.5 in urban area of Hong Kong[J]. Journal of hazardous materials, 2006, 138(1):73-85.
[16] Gao Y, Nelson E, Field M, et al. Characterization of atmospheric trace elements on PM2.5 particulate matter over the New York-New Jersey harbor estuary[J]. Atmospheric Environment, 2002, 36(6):1077-1086.
[17] Tang WC, Jin LX, Zhou XM. Reference geochemical values of elements in soil of Chengdu city and their implications[J]. Geophysical and Geochemical Exploration, 2005, 29(1):71-83 (in Chinese). 唐文春, 金立新, 周雪梅. 成都市土壤中元素地球化学基准值研究及其意义[J]. 物探与化探, 2005, 29(1): 71-83.
[18] Veysseyre A, Moutard K, Ferrari C, et al. Heavy metals in fresh snow collected at different altitudes in the Chamonix and Maurienne valleys, French Alps: initial results[J]. Atmospheric Environment, 2001, 35(2): 415-425.
[19] Wang QY, Cao JJ, Shen ZX, et al. Chemical characteristics of PM2.5 during dust storms and air pollution events in Chengdu, China[J]. Particuology, 2013, 11(1): 70-77.
[20] Lough GC, Schauer JJ, Park JS, et al. Emissions of metals associated with motor vehicle roadways[J]. Environmental Science & Technology, 2005, 39(3):826-836.
[21] Sternbeck J, Sjdin A, Andréasson K. Metal emissions from road traffic and the influence of resuspension:results from two tunnel studies[J]. Atmospheric Environment, 2002, 36(30):4735-4744.
[22] Xu M, Yan R, Zheng C, et al. Status of trace element emission in a coal combustion process: a review[J]. Fuel Processing Technology, 2004, 85(2):215-237.
[23] Querol X, Viana M, Alastuey A, et al. Source origin of trace elements in PM from regional background, urban and industrial sites of Spain[J]. Atmospheric Environment, 2007, 41(34): 7219-7231.
/
| 〈 |
|
〉 |