期刊文献+

基于被动采样技术的垃圾焚烧厂及周边大气中PAHs分布研究 被引量:4

Pilot Study on PAHs of the Atmosphere Around the Refuse Incineration Plant Based on the Technology of Passive Sampling
原文传递
导出
摘要 垃圾焚烧是大气PAHs污染的重要来源,为监测垃圾焚烧过程产生的PAHs,利用被动采样技术对垃圾焚烧厂及周边大气中的多环芳烃(PAHs)进行了定量分析.结果表明,PAHs总量为146.29~396.30 ng·d-1,其中气相中PAHs为128.03~377.05 ng·d-1,颗粒相中PAHs为10.698~19.251 ng·d-1.气相中PAHs组成以菲、荧蒽、芴等低环化合物为主,菲的含量高达55.1%.选定松针作为被动植物样品,测得松针中PAHs的浓度为651.88~1 044.43 ng·g-1;考察土壤中PAHs的分布特征,测得土壤中PAHs浓度为35.04~998.89 ng·g-1.被动采样和松针、土壤中所含的PAHs分布特征相似,说明被动采样能反映PAHs在环境中的真实积累情况.此外,通过比较主动采样与被动采样结果,表明两者对大气中PAHs的富集能达到基本一致的效果. Waste incineration is the main source of PAHs pollution of the atmosphere.In order to monitor the PAHs produced during the process of incineration,methods of quantitatively analysis for the PAHs of the atmosphere around the refuse incineration plant has been used on the basis of passive sampling technology.The result shows that the quantum of PAHs ranged 146.29-396.30 ng·d^-1,among which gaseous phase ranged 128.03-377.05 ng·d^-1,particulate phase ranged 10.698-19.251 ng·d^-1.Low ring compounds like phenanthrene,fluoranthene,fluorene make up the most of PAHs of gaseous phase in the atmosphere,in which phenanthrene reaches up to 55.1%.Pine needles are picked as passive plant samples,and the result shows that the concentration of PAHs in pine needles ranged 651.88-1 044.43 ng·g-1.The distribution characteristics of PAHs in the soil reveals that the concentration of PAHs in the soil ranged 35.04-998.89 ng·g-1.The PAHs distributions in passive sampling,pines and soil are extremely similar,which indicates that the passive samplings can reflect the real PAHs accumulation conditions in the environment.Besides,the results of passive sampling were compared with active sampling,and both accumulation abilities work almost the same.
出处 《环境科学》 EI CAS CSCD 北大核心 2012年第11期4018-4024,共7页 Environmental Science
关键词 分布 大气 多环芳烃 被动采样 垃圾焚烧 distribution atmosphere polycyclic aromatic hydrocarbons passive sampling waste incineration
  • 相关文献

参考文献23

  • 1刘敏,许世远.长江口潮滩POPs环境生物地球化学过程与生态风险[M].北京:中国环境科学出版社,2005:1-15.
  • 2Neff J M. Polycyclic aromatic hydrocarbons in the aquaticenvironment[ M ].London : Applied Science Publishers, 1982.385-409.
  • 3Wheatley L, Levendis Y A, Vouros P. Exploratory study on thecombustion and PAH emissions of selected municipal wasteplastics[ J].Environmental Science and Technology, 1993 , 27(13): 2885-2893.
  • 4祁明峰.燃烧过程中多环芳烃的生成与数值模拟[D].杭州:浙江大学,2003.
  • 5Sawieki E , Elbert W C , Hauser T R,eZ al. Benzo (a) pyrenecontent of the air of American communities [ J ].AmericanIndustrial Hygiene Association Journal, 1960,21(6) : 443-451.
  • 6Buehler S S’ Basu I,Hites R A. A comparison of PAH, PCB ,and pesticide concentrations in air at two rural sites on LakeSuperior[ J].Environmental Science and Technology, 2001,35(12): 2417-2422.
  • 7Coleman P J,Lee R G M, Aleoek R E, et al. Observations onPAH, PCB, and PCDD/F trends in U. K. urban air, 1991-1995 [ J ].Environmental Science and Technology, 1997, 31(7): 2120-2124.
  • 8Ngabe B, Poissant L. Polycyclic aromatic hydrocarbons in the airin the St. Lawrence Basin ( Quebec) [ J].Environmental Scienceand Technology, 2003,37(10) : 2094-2099.
  • 9李军,张干,祁士华.广州市大气中多环芳烃分布特征、季节变化及其影响因素[J].环境科学,2004,25(3):7-13. 被引量:69
  • 10Wang W T, Simonich S L M, Wang W, et al. Atmosphericpolycyclic aromatic hydrocarbon concentrations and gas/particlepartitioning at background, rural village and urban sites in theNorth China Plain [ J ].Atmospheric Research,2011 , 99 ( 2 ):197-206.

二级参考文献51

  • 1刘国卿,张干,李军,彭先芝,祁士华.利用SPMD技术监测珠江三角洲大气中多环芳烃[J].中国环境科学,2004,24(3):340-344. 被引量:6
  • 2李军,张干,祁士华,刘国卿.广州市大气中颗粒态多环芳烃(PAHs)的主要污染源[J].环境科学学报,2004,24(4):661-666. 被引量:44
  • 3刘向,张干,刘国卿,李军,彭先芝,张力,李向东,祁士华,邹世春.南岭北坡苔藓中多环芳烃的研究[J].中国环境科学,2005,25(1):101-105. 被引量:18
  • 4成玉,盛国英,傅家谟,闵育顺.大气气溶胶中多环芳烃的定量分析[J].环境化学,1996,15(4):360-365. 被引量:51
  • 5[1]Strand A, Hov é. A model strategy for the simulation of chlorinated hydrocarbon distribution in the global environment[J]. Water, Air and Soil Pollution, 1996, 86: 283~316.
  • 6[2]Nelson E D, Mcconnell L L, Baker J E. Diffusive exchange of gaseous polycyclic aromatic hydrocarbons and polychlorinated biphenyls across the air-water interface of the Chesapeake Bay[J]. Environ Sci Technol, 1988, 22: 912~919.
  • 7[3]Sims R C, Overcash M R. Fate of polycyclic aromatic compounds (PNAs) in soil-plant system[J]. Residue Reviews, 1983, 88: 1~68.
  • 8[4]Bidleman T E. Atmospheric processes: wet and dry deposition of organic compounds are controlled by their vapor/particle partitioning[J]. Environ Sci Technol, 1988, 22: 361~367.
  • 9[5]Pankow J F. Review and comparative analysis of the theories on partitioning between the gas and aerosol particulate phases in the atmosphere[J]. Atmos Environ, 1987, 21: 2275~2283.
  • 10[9]William E C, Terry F B. Polycyclic aromatoc hydrocarbons and polychlorinated biphenyls in air at an urban and a rural site near lake Michigan[J]. Environ Sci Technol, 1995, 29: 2782~2789.

共引文献91

同被引文献76

引证文献4

二级引证文献24

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部