煤矸石堆积下多环芳烃的淋溶污染特征

王新伟, 钟宁宁, 韩习运. 煤矸石堆积下多环芳烃的淋溶污染特征[J]. 环境工程学报, 2013, 7(9): 3594-3600.
引用本文: 王新伟, 钟宁宁, 韩习运. 煤矸石堆积下多环芳烃的淋溶污染特征[J]. 环境工程学报, 2013, 7(9): 3594-3600.
Wang Xinwei, Zhong Ningning, Han Xiyun. Leaching pollution characteristics of polycyclic aromatic hydrocarbons from piled coal gangue[J]. Chinese Journal of Environmental Engineering, 2013, 7(9): 3594-3600.
Citation: Wang Xinwei, Zhong Ningning, Han Xiyun. Leaching pollution characteristics of polycyclic aromatic hydrocarbons from piled coal gangue[J]. Chinese Journal of Environmental Engineering, 2013, 7(9): 3594-3600.

煤矸石堆积下多环芳烃的淋溶污染特征

  • 基金项目:

    平顶山煤业集团科研基金资助项目

  • 中图分类号: X75

Leaching pollution characteristics of polycyclic aromatic hydrocarbons from piled coal gangue

  • Fund Project:
  • 摘要: 淋溶是使有害物质析出的主要途径之一。为查明煤矸石堆放淋溶造成的有机污染效应,对不同风化强度煤矸石进行了动态淋溶模拟实验,系统研究了煤矸石中US EPA优先控制的16种多环芳烃(PAH16)的析出规律和迁移方式。获得煤矸石中多环芳烃(PAHs)淋溶特征如下:煤矸石堆积期遭受短期降雨(500~1 600 mm)作用后,煤矸石溶出的PAH16总质量浓度达125.6~451.2 ng/L。PAH16溶出量初期较高,在一定降雨期后又达到峰值,酸雨条件下,煤矸石山淋溶出的PAH16可由线性累加转为指数快速累加的趋势。淋溶液中优势组分为萘、二氢苊、芴和菲,4种组分之和占所测PAHs总量的80%~90%。煤矸石溶出的PAHs环数分布为2环>3环>4环>5环、6环。迁移方式上,2环PAHs多以溶解相迁移,3环PAHs主要以颗粒态迁移,存在少量溶解形式,而4环以上PAHs则以颗粒相形式迁移。
  • 加载中
  • [1] Binotto R. B., Teixeira E. C., Sanchez J. C. D., et al. Environmental assessment: contamination of phreatic aquifer in areas impacted by waste from coal processing activities. Fuel, 2000, 79(2):1547-1560
    [2] Szczepanska J., Twardowska I. Distribution and environmental impact of coal mining wastes in upper silesia. Poland Environmental Geology, 1999, 38 (3): 249-258
    [3] 吴代赦, 郑宝山, 康往东, 等. 煤矸石的淋溶行为与环境影响的研究—以淮南潘谢矿区为例. 地球与环境, 2004, 32(1): 55-59 Wu D. S., Zheng B. S., Kang W. D., et al. Leaching behavior of coal spoils and environmental impacts. Earth and Environment, 2004, 32(1): 55-59(in Chinese)
    [4] 肖利萍, 梁冰, 黑瑞卿, 等. 煤矸石浸泡污染物溶解释放规律研究(二):不同风化煤矸石在不同酸度条件下浸泡实验. 科学技术与工程, 2006, 6(7): 844-847 Xiao L.P., Liang B., Hei R.Q., et al. Contamination releasing mechanism research of coal gangue in diferent acidity soaking. Science Technology and Engineering, 2006, 6(7): 844-847(in Chinese)
    [5] 张俊,张生,李畅游,等. 基于土柱淋滤实验的煤矸石饱和状态下溶质释放过程研究. 煤田地质与勘探, 2012, 4(5):56-59 Zhang J., Zhang S., Li C. Y., et al. Coal gangue saturated solute release process based on the soil column leaching experiments. Coal Geology & Exploration, 2012, 4(5):56-59(in Chinese)
    [6] 胡振琪, 王萍, 张明亮, 等. 土工布阻隔煤矸石中重金属迁移实验研究. 环境工程学报, 2008, 2(4): 536-541 Hu Z. Q., Wang P., Zhang M. L., et al. A column test for preventing heavy metal pollutionfrom coal gangue with geotextiles. Chinese Journal of Environmental Engineering, 2008, 2(4):536-541 (in Chinese)
    [7] Yellishetty M., Ranjith P. G., Kumar D. L. Metal concentrations and metal mobility in unsaturated mine wastes in mining areas of Goa. India Resources, Conservation and Recycling, 2009, 53(7): 379-385
    [8] 梁冰, 薛强, 刘晓丽. 煤矸石中硫酸盐对地下水污染的环境预测. 煤炭学报, 2003, 28(5):527-530 Liang B.,Xue Q., Liu X. L. Environmental prediction on coal mine spoil of sulphateck for groundwater pollution. Journal of China Coal Society, 2003, 28(5):527-530(in Chinese)
    [9] 付天岭, 吴永贵, 欧莉莎, 等.不同氧化还原环境对煤矸石污染物质释放的影响. 环境科学学报, 2012, 32(10): 2476-2482 Fu T.L., Wu Y.G., Ou L.S., et al. Effects of different redox environments on the release of coal gangue contaminants. Acta Scientiae Circumstantiae, 2012, 32(10): 2476-2482(in Chinese)
    [10] Zhao Z. B., Liu K.L., Xie W., et al. Soluble polycyclic aromatic hydrocarbons in raw coals. Journal of Hazardous Materials, 2000, 73(1):77-85
    [11] 薛剪, 刘桂建, 张浩原, 等. 提取时间对提取原煤中多环芳烃的影响. 环境科学研究, 2006, 19(5):107-112 Xue J., Liu G.J., Zhang H.Y., et al. The impact of PAHs extracted from raw coal in different times. Research of Environmental Sciences, 2006, 19(5):107-112(in Chinese)
    [12] 张建立,潘懋,钟佐燊,等. 山东淄博煤矿区环境中多环芳烃的初步研究. 煤田地质与勘探, 2002, 30(2): 7-9 Zhang J.L., Pan M., Zhong Z. S. Initial research on polycyclic aromatic hydrocarbons in Zibo coal mine environment. Coal Geology & Exploration, 2002, 30(2): 7-9(in Chinese)
    [13] 邓寅生, 何莎莎, 韩哲楠. 粉煤灰井下填充时PAHs对地下水环境的影响. 环境工程学报, 2007, 1(6):109-113 Deng Y.S.,He S.S., Han Z.N. Impact of PAHs on groundwater during mine-filling with fly ash.Chinese Journal of Environmental Engineering, 2007, 1(6):109-113(in Chinese)
    [14] 余运波, 汤鸣皋, 钟佐燊, 等. 煤矸石堆放对水环境的影响——以山东省一些煤矸石堆为例. 地学前缘, 2001, 8(1):163-169 Yu Y.B., Tang M.G., Zhong Z. S., et al. The influence of coal mining waste piles on hydro-environment in Shandong province.Earth Science Frontiers (China University of Geosciences,Beijing), 2001, 8(1):163-169(in Chinese)
    [15] Wang X. W., Zhong N.N., Hu D.M., et al. Polycyclic aromatic hydrocarbon(PAHs) pollutants in groundwater from coal gangue stack area: Characteristics and origin. Water Science & Technology, 2009, 59(5): 1043-1051
    [16] Hodson M. E., Langan S. J. A long-term soil leaching column experiment investigating the effect of variable sulphate loads on soil solution and soil drainage chemistry. Environmental Pollution, 1999, 104(1): 11-19
    [17] Pedit J. A., Miller C. T., Weber W. J., et al. A distributed reactivity model for sorption by soil and sediments.4. Intraparticle heterogeneity and phase distribution relationships under nonequilibrium conditions. Environ. Sci. Technol., 1996, 30(10): 3128-3131
    [18] Xing B., Pignatello J. J., Gigliotti B. Competitive sorption between atrazine and other organic compounds in soils and model sorbents. Environ. Sci. Technol., 1996, 30(8): 2432-2440
    [19] Kan A. T., Fu G., Tomson M. B. Adsorption/desorption hysteresis in organic pollutant and soil/sediment interaction. Environ. Sci. Technol., 1994, 28 (5): 859-867
    [20] Ghosh U., Jeffrey W. T., Richard G. L. Particle-scale investigation of PAH desorption kinetics and thermodynamics from sediments. Environ. Sci. Technol., 2001, 35(17): 3468-3475
    [21] 陈静, 胡俊栋, 王学军. 混合溶剂解吸土壤中多环芳烃的研究.中国环境监测, 2004, 20(6): 16-20 Chen J., Hu J. D., Wang X. J. The adsorption of PAHs from contaminated soil with mixed solves. Environmental Monitoring in China, 2004, 20(6): 16-20 (in Chinese)
    [22] Kim Y. J., Osako M. Leaching characteristics of polycyclic aromatic hydrocarbons (PAHs) from spiked sandy soil. Chemosphere, 2003, 51(5): 387-395
    [23] Brandt H.C.A., Degroot P.C.Aqueous leaching of polycyclic aromatic hydrocarbons from bitumen and asphalt. Water Res., 2001,35(17):4200-4207
    [24] 陈静, 王学军, 陶澍, 等. 天津地区土壤多环芳烃在剖面中的纵向分布特征. 环境科学学报, 2004, 24(2): 286-290 Chen J., Wang X.J., Tao S., et al. Vertical distribution of polycyclic aromatic hydrocarbons in soils in Tianjin Area. Acta Scientiae Circumstantiae, 2004, 24(2): 286-290(in Chinese)
    [25] Jung-Won M., Goltz M. N., Kyu-Hong A., et al. Dissolved organic matter effects on the performance of a barrier to polycyclic aromatic hydrocarbon transport by groundwater. Journal of Contaminant Hydrology, 2003, 60(3-4): 307-326
    [26] Chiou C.T., Malcolm R. L., Brinton T. I., et al. Water solubility enhancement of some organic Polluatnts and pesticides by dissolved humic and fulvic acids. Environ. Sci. Technol., 1986, 20(5): 502-508
    [27] Raber B., Kögel-Knaber, Stein C., et al. Partitioning of polycyclic aromatic hydrocarbons to dissolved organic matter from different soils.Chemosphere, 1998, 36(1): 79-97
  • 加载中
计量
  • 文章访问数:  2074
  • HTML全文浏览数:  1133
  • PDF下载数:  1110
  • 施引文献:  0
出版历程
  • 收稿日期:  2013-05-03
  • 刊出日期:  2013-09-15

煤矸石堆积下多环芳烃的淋溶污染特征

  • 1. 中国石油大学(北京)油气资源与探测国家重点实验室, 北京 102249
  • 2. 平顶山煤业(集团)有限责任公司勘探工程处, 平顶山 467000
基金项目:

平顶山煤业集团科研基金资助项目

摘要: 淋溶是使有害物质析出的主要途径之一。为查明煤矸石堆放淋溶造成的有机污染效应,对不同风化强度煤矸石进行了动态淋溶模拟实验,系统研究了煤矸石中US EPA优先控制的16种多环芳烃(PAH16)的析出规律和迁移方式。获得煤矸石中多环芳烃(PAHs)淋溶特征如下:煤矸石堆积期遭受短期降雨(500~1 600 mm)作用后,煤矸石溶出的PAH16总质量浓度达125.6~451.2 ng/L。PAH16溶出量初期较高,在一定降雨期后又达到峰值,酸雨条件下,煤矸石山淋溶出的PAH16可由线性累加转为指数快速累加的趋势。淋溶液中优势组分为萘、二氢苊、芴和菲,4种组分之和占所测PAHs总量的80%~90%。煤矸石溶出的PAHs环数分布为2环>3环>4环>5环、6环。迁移方式上,2环PAHs多以溶解相迁移,3环PAHs主要以颗粒态迁移,存在少量溶解形式,而4环以上PAHs则以颗粒相形式迁移。

English Abstract

参考文献 (27)

目录

/

返回文章
返回