北京市冬季道路沉积物中多环芳烃的污染特征和源解析
Pollution characteristics and source apportionment of polycyclic aromatic hydrocarbons (PAHs) in road sediments of Beijing in winter
-
摘要: 在北京城区四环以内采集了33个冬季道路沉积物样品,分析其中多环芳烃(PAHs)的含量、分布特征、来源和生态风险.结果表明,16种多环芳烃(PAHs)∑16 PAHs的浓度范围为931.0-2668.7 ng·g-1干重,平均浓度为1602.4 ng·g-1干重,污染物的组成以4环和3环PAHs为主.通过LMW/HMW(低分子量与高分子量PAHs的比值)法、特征比值法和主成分分析法得出,道路沉积物中PAHs主要来自于煤、化石燃料的燃烧以及交通尾气的排放.由TEQBaP分析结果可知,33个采样点PAHs的∑16TEQBaP范围为58.2-324.4 ng·g-1干重,平均值为139.3 ng·g-1干重;所有采样点的∑10TEQBaP范围为33.1-266.8 ng·g-1干重,平均值为95.0 ng·g-1干重,均超过荷兰土壤的目标参考值,说明北京市冬季道路沉积物中PAHs存在潜在的生态风险;其中7种致癌性PAHs(BaA、Chr、BbF、BkF、BaP、IPY和DBA)的TEQBaP占∑16TEQBaP的96.1%-99.3%,平均值为98.5%,是∑16TEQBaP的主要贡献者,并且BaP的贡献率最大.Abstract: Thirty-three road sediment samples within the Fourth Ring of Beijing were collected in the winter, the concentrations, distribution characteristics, sources and ecological risk of polycyclic aromatic hydrocarbons (PAHs) were analysed. Results showed that the total concentrations of 16 PAHs in the road sediments ranged from 931.0 ng·g-1 to 2668.7 ng·g-1 dry weight, and the average concentration was 1602.4 ng·g-1 dry weight. The composition characteristics of pollutants showed that 4- and 3-ring PAHs were the dominant compounds. The LMW/HMW(Ratio of low molecular weight to high molecular weight PAHs), characteristics ratios and principal component analysis indicated that PAHs in the road sediments mainly derived from coal, and fossil fuel combustion and automobile emission. Based on PAHs toxic equivalent concentration (TEQBaP), the total TEQBaP of 16 PAHs in 33 road sediment samples ranged from 58.2 ng·g-1 to 324.4 ng·g-1 dry weight, and the average value was 139.3 ng·g-1 dry weight. The total TEQBaP of 10 PAHs in all samples ranged from 33.1 to 266.8 ng·g-1 dry weight, and the average value was 95.0 ng·g-1 dry weight, which all exceeded the reference value of Holland soil, suggesting that there was a potential ecological risk of PAHs in road sediments of Beijng. Seven highly carcinogenic PAHs(BaA, Chr, BbF, BkF, BaP, IPY and DBA) were the main contributors to the total TEQBaP of 16 PAHs, which accounted for 96.1% to 99.3%, with an average value of 98.5%, and the contribution rate of BaP was the most.
-
-
[1] DURANT J L,BUSBY W F,LAFLEUR A L,et al.Human cell mutagenicity of oxygenated,nitrated and unsubstituted polycyclic aromatic hydrocarbons associated with urban aerosols[J].Mutation Research/Fundamental and Molecular Mechanisms of Mutagenesis,1997,371(3):123-157. [2] 王桂山,仲兆庆,王福寿.PAH (多环芳烃)的危害及产生途径[J].山东环境,2001,41(20):41-46. WANG G S,ZHONG Z Q,WANG F S.Hazards of PAH (polycyclic aromatic hydrocarbons) and the way of production[J].Shandong Environment,2001,41(20):41-46(in Chinese).
[3] 彭驰,王美娥,廖晓兰.城市土壤中多环芳烃分布和风险评价研究进展[J].应用生态学报,2010,21(2):514-522. PENG C,WANG M E,LIAO X L.Distribution and risk assessment of polycyclic aromatic hydrocarbons in urban soils:A review[J].Chinese Journal of Applied Ecology,2010,21(2):514-522(in Chinese).
[4] 赵靖宇,王文涛,王伟,等.华北地区城镇多环芳烃干沉降特征[J].环境科学学报,2009,29(7):1358-1362. ZHAO J Y,WANG W T,WANG W.Dry deposition of polycyclic aromatic hydrocarbons in cities and towns of Northern Chinese[J].Acta Scientiae Circumstantiae,2009,29(7):1358-1362(in Chinese).
[5] 冯精兰,刘书卉,申君慧,等.新乡市道路灰尘中PAHs的污染特征和来源解析[J].环境化学,2013,32(4):630-639. FENG J L,LIU S H,SHEN J H,et al.Pollution characteristics and sources of PAHs in road dust in Xinxiang City[J].Environmental Chemistry,2013,32(4):630-639(in Chinese).
[6] BERGER J,DENBY B.A generalised model for traffic induced road dust emissions.Model description and evaluation[J].Atmospheric Environment,2011,45(22):3692-3703. [7] HASSANIEN M A,ABDEL-LATIF N M.Polycyclic aromatic hydrocarbons in road dust over Greater Cairo,Egypt[J].Journal of Hazardous Materials,2008,151(1):247-254. [8] BOONYATUMANOND R,MURAKAMI M,et al.Sources of polycyclic aromatic hydrocarbons (PAHs) in street dust in a tropical Asian mega-city,Bangkok,Thailand[J].Science of the Total Environment,2007,384(l-3):420-432. [9] ZHANG W,ZHANG S,WANG C,et al.Source diagnostics of polycyclic aromatic hydrocarbons in urban road runoff,dust,rain and canopy throughfall[J].Environmental Pollution,2008,153(3):594-601. [10] WATANABE H,NAKAJIMA F,KASUGA I,et al.Toxicity evaluation of road dust in the runoff process using a benthic ostracod Heterocypris incongruens[J].Science of the Total Environment,2011,409(12):2366-2372. [11] 程书波,刘敏,欧冬妮,等.上海市地表灰尘中PAHs的来源辨析[J].中国环境科学,2007,27(5):589-593. CHENG S B,LIU M,OU D N,et al.Source identification of PAHs in road dusts from Shanghai city[J].China Environmental Science,2007,27(5):589-593(in Chinese).
[12] BROWN J N,PEAKE B M.Sources of heavy metals and polycyclic aromatic hydrocarbons in urban stormwater runoff[J].Science of the Total Environment,2006,359:145-155. [13] RUCHAYA B,MICHIO M,GULLAYA W,et al.Sources of polycyclic aromatic hydrocarbons (PAHs) in street dust in a tropical Asian mega-city,Bangkok,Thailand[J].Science of the Total Environment,2007,348(1-3):420-432. [14] DONG T T T,LEE B K.Characteristics,toxicity,and source apportionment of polycyclic aromatic hydrocarbons (PAHs) in road dust of Ulsan,Korea[J].Chemosphere,2009,74:1245-1253. [15] MALISZEW-KORDYBACH B.Polycyclic aromatic hydrocarbons in agricultural soils in Poland:Preliminary proposals for criteria to evaluate the level of soil contamination[J].Applied Geochemistry,1996,11:121-127. [16] SOCLO H H,GARRIGUES P,EWALD M.Origin of polycyclic aromatic hydrocarbons (PAHs) in costal marine sediments:Case studies in Cotonou (Benin) and Aquitaine (France) areas[J].Marine Pollution Bulletin,2000,40:387-396. [17] ROCHER V,AZIMI S,MOILLIERON R,et al.Hydrocarbons and heavy metals in the different sewer deposits in the Le Marais'catchment (Paris,France):Stocks,distributions and origins[J].Science of the Total Environment,2004,323:107-122. [18] WILCKE W,AMELUNG W,MARTIUS C,et al.Biological sources of polycyclic aromatic hydrocarbons in the Amazonian rain forest[J].Journal of Plant Nutrition and Soil Science,2000,163(1):27-30. [19] 李勇,董娴,张颂富,等.百花湖水库表层沉积物中PAHs生态风险评价[J].湖北农业科学,2013,52(6):1281-1283. LI Y,DONG X,ZHAN S F,el ta.Ecological risk assessment of PAHs in surface sediments from baihua reservoir,Guizhou Province[J].Hubei Agricultural Sciences,2013,52(6):1281-1283(in Chinese).
[20] YUNKER M B,MACDONALD R W,VINGARZAN R,et al.PAHs in the Fraser River Basin:A critical appraisal of PAH ratios as indicators of PAH source and composition[J].Organic geochemistry,2002,32:489-515. [21] 张天彬,万洪富,周健民,等.深圳表层土壤中多环芳烃的污染特征及来源[J].生态环境,2008,17(3):1032-1036. ZHANG T B,WAN H F,ZHOU J M,et al.Pollution characteristics and sources of polycyclic aromatic hydrocarbons in surface soil of Shenzhen[J].Ecology and Environment,2008,17(3):1032-1036(in Chinese).
[22] HWANG H M,WADE T L,SERIEANO J L.Concentrations and source characterization of polycyclic aromatic hydrocarbons in pine needles from Korea,Mexico,and United States[J].Atmospheric Environment,2003,37(16):2259-2267. [23] JIANG Y F,WANG X T,WANG F,et al.Levels,composition profiles and sources of polycyclic aromatic hydrocarbons in urban soil of Shanghai,China[J].Chemosphere,2009,75(8):1112-1118. [24] DUVAL M M,FRIENDLANDER S K.Source resolution of polycyclic aromatic hydrocarbons in the Los Angeles atmospheres:Application of a CMB with first order decay[R].U.S.EPA report EPA-600/2-81-161,Washington,DC. [25] ZAKARIA M P,TAKADA H,TSUTSUMI S,et al.Distribution of polycyclic aromatic hydrocarbons (PAHs) in riverine and estuarine in Malaysia:A widespread input of petrogenic PAHs[J].Environmental Science and Technology,2002,36(9):907-1918. [26] BOONYATUMANOND R,WATTAYAKOM G,TOGO A,et al.Distribution and origins of polycyclic aromatic hydrocarbons (PAHs) in riverine,estuarine and marine sediments in Thailand[J].Marine Pollution Bulletin,2006,52(8):942-956. [27] FRASER M P,CASS G R,SIMONEIT B R T,et al.Air quality model evaluation data for organics.4.C2-C36 non-aromatic hydrocarbons[J].Environmental Science and Technology,1997,31(8):2356-2367. [28] GUO H,LEES,HO K,et al.Particle-associated polycyclic aromatic hydrocarbons in urban air of Hong Kong[J].Atmospheric Environment,2003,37(38):5307-5317. [29] RAVINDRA K,SOKHI R,VAN GRIEKEN R.Atmospheric polycyclic aromatic hydrocarbons:Source attribution,emission factors and regulation[J].Atmospheric Environment,2008,42(13):2895-2921. [30] 段永红,陶澍,王学军,等.天津表土中多环芳烃含量的空间分布特征与来源[J].土壤学报,2005,42(6):942-947. DUAN Y H,TAO S,WANG X J,et al.Spatial distribution and sources of PAHs in surface soils of Tianjin[J].Acta Pedologica Sinica,2005,42(6):942-947(in Chinese).
[31] DOUBEN P E T.PAHs:An Ecotoxicological Perspective[M].New York:Wiley,2003:377. [32] 于国光,叶雪珠,赵首萍,等.杭州市郊区表层土壤中多环芳烃的风险分析[J].生态环境学报,2011,20(5):966-969. YU G G,YE X Z,ZHAO S P,et al.Risk analysis of polycyclic aromatic hydrocarbons in the surface soil of Hangzhou suburbs[J].Ecology and Environmental Sciences,2011,20(5):966-969(in Chinese).
[33] WITT G.Polycyclic aromatic hydrocarbons in water and sediment of the Baltic Sea[J].Marine Pollution Bulletin,1995,31(4/12):237-248. [34] 王伟.鞍山市大气中多环芳烃健康影响评价[J].环境科学与管理,2013,38(6):192-194. WANG W.Health Impact Assessment of PAHs on atmosphere of Anshan[J].Environmental Science and Management,2013,38(6):192-194(in Chinese).
[35] WANG Z,CHEN J W,YANG P,et al.Polycyclic aromatic hydrocarbons in Dalian soils:Distribution and toxicity assessment[J].Journal of Environmental Monitoring,2007,9(2):199-204. [36] JIANG Y F,HU X F,UWAMUNGUJ.YVES,et al.Status,source and health risk assessment of polycyclic aromatic hydrocarbons in street dust of an industrial city,NW China[J].Ecotoxicology and Environmental Safety,2014,106:11-18. [37] [38] LE H T,NGUYEN M T,GO S et al.Aryl hydrocarbon receptor mediated activities in road dust from a metropolitan area,Hanoi-Vietnam:Contribution of polycyclic aromatic hydrocarbons (PAHs) and human risk assessment[J].Science of the Total Environment,2014,491-492:246-254. -

计量
- 文章访问数: 901
- HTML全文浏览数: 832
- PDF下载数: 438
- 施引文献: 0