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为了解下垫面对径流中多环芳烃( PAHs)污染特征的影响,对4次降雨事件中不同下垫面地表径流中的PAHs污染特征进行了分析.研究发现,屋面( A点)与交通路面( C点)的PAHs污染负荷远远大于另两种下垫面,降雨事件平均浓度分别达到26.66μg·L-1和27.87μg·L-1.各场降雨事件都存在随着降雨历时污染物浓度逐渐降低的过程,其中交通路面变化最为剧烈,PAHs浓度由初始的33.50μg·L-1经90 min后下降至16.36μg·L-1,而屋面则在径流结束前伴有浓度回升的现象.径流中溶解态PAHs含量远低于颗粒态含量,以2—3环略占优势,达31%—42%;而在颗粒态 PAHs 中5—6环则相对更多.广场路面( B 点)和交通路面(C点)由于汇流面积较大,具有较明显的初期冲刷效应;屋面(A点)的冲刷效应相对较弱;草地(D点)则未表现出初期冲刷效应.研究结果表明下垫面对径流中PAHs的含量和消除均有一定影响,但与PAHs组分的相对比例无明显相关.

To understand the role of underlying surface in affecting the pollution characteristics of polycyclic aromatic hydrocarbons ( PAHs) in urban runoff, we analyzed the PAHs contents in runoff samples from different underlying surfaces in 4 rainfall events. In the study, the PAHs contents in runoff from roof ( site A) and highway ( site C) were much higher than other underlying surfaces, and their concentrations were up to 26. 66 and 27. 87 μg·L-1, respectively. PAH concentrations decreased along with rainfall duration in all rainfall events. Among them, the contents of PAHs in highway runoff changed most dramatically, which declined from 33.50μg·L-1 down to 16.36μg·L-1 within 90 min. However, PAHs in runoff showed a unique concentration elevation near the end of the rainfall. The PAHs distribution analysis showed there were more particulate PAHs than dissolved PAHs in runoff. Furthermore, 2—3 ring PAHs ( 31%—42%) slightly edged other constituents in dissolved PAHs, while 5—6 ring PAHs were major components of particulate PAHs. With larger catchment areas, square ( site B) and highway ( site C) , had more obvious first initial effects. Roof ( site A) showed a weak first initial effect, and grassland ( site D) had no such effect. Our results suggested that the underlying surface had impacts on the contents and elimination of PAHs in runoff, but had little relation with the compositional distribution of PAHs.

参考文献

[1] 欧阳威,王玮,郝芳华,宋凯宇,王云慧.北京城区不同下垫面降雨径流产污特征分析[J].中国环境科学,2010(09):1249-1256.
[2] 徐祖信,黄沈发,鄢忠纯.上海市非点源污染负荷研究[J].上海环境科学,2003(z1):112-116,130.
[3] 夏宏生,林芳莉.广州市城区降雨径流水质特征分析[J].环境科学与管理,2010(05):129-131,150.
[4] Hoffman E J;Mills G L;Latimer J S et al.Urban runoff as a source of polycyclic aromatic hydrocarbons to coastal waters[J].Environmental Science and Technology,1984,18(8):580-587.
[5] Daane LL;Harjono I;Zylstra GJ;Haggblom MM .Isolation and characterization of polycyclic aromatichydrocarbon-degrading bacteria associated with the rhizosphere of saltmarsh plants[J].Applied and Environmental Microbiology,2001(6):2683-2691.
[6] Scheepers PT;van Houtum J;Anzion RB .The occupational exposure of dermatology nurses to polycyclic aromatic hydrocarbons - evaluating the effectiveness of better skin protection.[J].Scandinavian journal of Work, Environment and Health,2009(3):212-221.
[7] Ouyang Wei;Guo BoBo;Hao FangHua;Huang HaoBo;Li JunQi;Gong YongWei.Modeling urban storm rainfall runoff from diverse underlying surfaces and application for control design in Beijing.[J].Journal of Environmental Management,2012:467-473.
[8] Mingteh Chang;Matthew W. McBroom;R. Scott Beasley .Roofing as a source of nonpoint water pollution[J].Journal of Environmental Management,2004(4):307-315.
[9] Lye, DJ .Rooftop runoff as a source of contamination: A review[J].Science of the Total Environment,2009(21):5429-5434.
[10] Gromaire MC.;Saad M.;Chebbo G.;Garnaud S. .Contribution of different sources to the pollution of wet weather flows in combined sewers[J].Water research: A journal of the international water association,2001(2):521-533.
[11] 莫文锐,田森林,黄建洪,杨宗慧.百年一遇大旱后城市雨水及降雨径流重金属污染调查[J].环境化学,2011(09):1676-1677.
[12] Z. Polkowska;T. Gorecki;J. Namiesnik .Quality of roof runoff waters from an urban region (Gdansk, Poland)[J].Chemosphere,2002(10):1275-1283.
[13] 谢继锋,胡志新,徐挺,韩红艳,尹大强.合肥市不同下垫面降雨径流水质特征分析[J].中国环境科学,2012(06):1018-1025.
[14] HJ 494-2009.水质采样技术指导[S].北京:中国标准出版社,2009.
[15] HJ 478-2009.水质-多环芳烃的测定液液萃取和固相萃取高效液相色谱法[S].北京:中国环境科学出版社,2009.
[16] 李静静,李云飞,谢继锋,徐挺,窦月芹.中空纤维膜液相微萃取与GC-MS联用测定地表径流中的多环芳烃[J].环境化学,2013(11):2170-2175.
[17] Patrick L. Brezonik;Teresa H. Stadelmann .Analysis and predictive models of stormwater runoff volumes, loads, and pollutant concentrations from watersheds in the Twin Cities metropolitan area, Minnesota, USA[J].Water research: A journal of the international water association,2002(7):1743-1757.
[18] 侯立柱,丁跃元,冯绍元,张书函,陈建刚,廖日红.北京城区不同下垫面的雨水径流水质比较[J].中国给水排水,2006(23):35-38.
[19] Polycyclic aromatic hydrocarbons in recent sediments from a subtropical estuary in Brazil[J].Marine chemistry,2010(1/2):56.
[20] Wei Zhang;Shucai Zhang;Chao Wan;Dapan Yue;Youbin Ye;Xuejun Wang .Source diagnostics of polycyclic aromatic hydrocarbons in urban road runoff, dust, rain and canopy throughfall[J].Environmental Pollution,2008(3):594-601.
[21] Michio Murakami;Fumiyuki Nakajima;Hiroaki Furumai .Modelling of runoff behaviour of particle-bound polycyclic aromatic hydrocarbons (PAHs) from roads and roofs[J].Water research: A journal of the international water association,2004(20):4475-4483.
[22] 王建龙,刘强,冯伟.雨水径流对景观水体中多环芳烃污染特征的影响[J].环境化学,2012(09):1393-1398.
[23] Geiger W.Flushing effects in combined sewer systems[A].Lausanne,Switzerland,1987:40-46.
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