天然矿物组合材料渗透反应墙修复地下水镉污染

曾婧滢, 秦迪岚, 毕军平, 罗岳平, 朱润良, 廖希谷, 张建新, 吕焕哲. 天然矿物组合材料渗透反应墙修复地下水镉污染[J]. 环境工程学报, 2014, 8(6): 2435-2442.
引用本文: 曾婧滢, 秦迪岚, 毕军平, 罗岳平, 朱润良, 廖希谷, 张建新, 吕焕哲. 天然矿物组合材料渗透反应墙修复地下水镉污染[J]. 环境工程学报, 2014, 8(6): 2435-2442.
Zeng Jingying, Qin Dilan, Bi Junping, Luo Yueping, Zhu Runliang, Liao Xigu, Zhang Jianxin, Lü Runliang. Remediation of cadmium contaminated ground-water using natural mineral combination materials based permeable reactive barrier[J]. Chinese Journal of Environmental Engineering, 2014, 8(6): 2435-2442.
Citation: Zeng Jingying, Qin Dilan, Bi Junping, Luo Yueping, Zhu Runliang, Liao Xigu, Zhang Jianxin, Lü Runliang. Remediation of cadmium contaminated ground-water using natural mineral combination materials based permeable reactive barrier[J]. Chinese Journal of Environmental Engineering, 2014, 8(6): 2435-2442.

天然矿物组合材料渗透反应墙修复地下水镉污染

  • 基金项目:

    国土资源部公益性行业科研专项(201111016-1)

  • 中图分类号: X523

Remediation of cadmium contaminated ground-water using natural mineral combination materials based permeable reactive barrier

  • Fund Project:
  • 摘要: 实验模拟地下环境,以天然矿物材料石灰石、海泡石和膨润土作为可渗透反应墙(PRB)填充材料,采用正交实验法设计了16种可渗透反应器,研究了天然矿物组合材料组配对污染地下水模拟液中镉污染的修复效果、出水pH、有效孔隙度和渗透系数的影响,同时对机理进行了分析。实验结果显示,组合材料对镉去除率达99.8%以上,石灰石对处理效果贡献最大,增加石灰石用量,处理效果明显改善,当石灰石含量为10%及更高时,对含镉1.0 mg/L的污染地下水模拟液处理后镉浓度低于0.7 μg/L,达到地下水质量标准GB/T 14848-93规定的II类水质标准;石灰石用量的增加对渗透系数影响不大,但出水pH呈弱碱性(7
  • 加载中
  • [1] Salim R., Al-Subu M.M., Sahrhage E. Uptake of cadmium from water by beech leaves. J. Environ. Sci. Health A, 1992, 27(3): 602-627
    [2] 王佳佳, 马慧敏, 张田林. 新型多功能螯合树脂的合成及对水中Cd(Ⅱ)离子的吸附特征. 环境工程学报, 2013, 7(4): 1378-1382 Wang J.J., Ma H.M., Zhang T.L. Synthesis of multifunctional chelating resin and its adsorption properties for Cd(Ⅱ) in water.Chinese Journal of Environmental Engineering, 2013, 7(4): 1378-1382(in Chinese)
    [3] 罗锦洪, 郑丙辉, 付青, 等. 基于人体健康风险的水污染事件遗传性致癌物安全度研究. 环境科学, 2012, 33(2): 342-345 Luo J.H., Zheng B.H., Fu Q., et al. Safety concentration of genotoxic carcinogens in water pollution accident based on human health risk. Environmental Science, 2012, 33(2): 342-345(in Chinese)
    [4] Ashworth D.J., Alloway B.J.Soil mobility of sewage sludge-derived dissolved organic matter, copper, nickel and zinc. Environ. Pollution, 2004, 127(1): 137-144
    [5] Richards B.K., Steenhuis T.S., Peverly J.H., et al. Effect of sludge-processing mode, soil texture and soil pH on metal mobility in undisturbed soil columns under accelerated loading. Environ.Pollution,2000, 109(2):327-346
    [6] Hashim M. A., Mukhopadhyay S., Sahu J. N., et al. Remediation technologies for heavy metal contaminated groundwater. Journal of Environmental Management, 2011, 92(10): 2388-2388
    [7] 张永祥, 梁建奎, 王然, 等. 地下水PRB原位生物修复中一种释氧材料的改进技术及效果分析. 环境工程学报, 2012, 6(11): 3910-3914 Zhang J.X., Liang J.K., Wang R., et al. Application of improving oxygen releasing material in situ polluted groundwater PRB bioremediation. Chinese Journal of Environmental Engineering, 2012, 6(11): 3910-3914(in Chinese)
    [8] 崔海炜, 孙继朝, 张英, 等. 可渗透反应墙原位修复垃圾渗滤液污染地下水. 环境工程学报, 2012, 6(8): 2698-2704 Cui J.H., Sun J.C., Zhang Y., et al. In situ remediation of leachate-polluted groundwater with permeable reactive barrier technique. Chinese Journal of Environmental Engineering, 2012, 6(8): 2698-2704(in Chinese)
    [9] Kamolpornwijit W., Liang L., West O. R., et al. Preferential flow path development and its influence on long-term PRB performance: column study. Journal of Contaminant Hydrology, 2003, 66(3/4): 161-178
    [10] Thiruvenkatachari R., Vigneswaran S., Naidu R. Permeable reactive barrier for groundwater remediation. Journal of Industrial and Engineering Chemistry, 2008, 14(2): 145-156
    [11] Andrew D.H., Demond A. H. Long-term performance of zero-valent iron permeable reactive barriers: A critical review. Environmental Engineering Science, 2007, 24(4):401-423
    [12] David W. B., Ptacek C. J., Benner S. G., et al. Treatment of inorganic contaminants using permeable reactive barriers. Journal of Contaminant Hydrology, 2000, 45(1-2):123-137
    [13] Suponik, Tomasz. Groundwater treatment with the use of zero-valent iron in the permeable reactive barriers technology. Physicochemcal Problems of Mineral Processing, 2013,49(1):13-23
    [14] 孟庆玲, 任群, 王显胜, 等. 组合材料渗透反应墙对硝基苯污染地下水的修复研究. 北京大学学报(自然科学版), 2010,46(3):413-416 Meng Q.L., Ren Q., Wang X.H., et al. Research on remediation of nitrobenzene contaminated ground-water with combination materials of permeable reactive barrie. Acta Scientiarum Naturalium Universitatis Pekinensis, 2010, 46(3): 413-416(in Chinese)
    [15] Karapinar N., Donat R. Adsorption behaviour of Cu2+ and Cd2+ onto natural bentonite. Desalination, 2009, 249(1): 123-129
    [16] Sevgi Kocaoba. Adsorption of Cd(Ⅱ), Cr(Ⅲ) and Mn(Ⅱ) on natural sepiolite. Desalination, 2009, 224(1-3): 24-30
    [17] Hamidi A. A., Mohd N. A., Kamar S. A., et al. Heavy metals (Cd, Pb, Zn, Ni, Cu and Cr(Ⅲ)) removal from water in Malaysia: Post treatment by high quality limestone. Bioresource Technology, 2008, 99(6): 1578-1583
    [18] Ralph D. Ludwig, McGregor R. G., Blowes D. W., et al. A permeable reactive barrier for treatment of heavy metals. Ground Water, 2002,40(1): 59-66
    [19] Guerin T.F., Horner S., Mcgovern T.,et al. An application of permeable reactive barrier technology to petroleum hydrocarbon contaminated groundwater. Water Research, 2002, 36(1): 15-24
    [20] 孙约兵,徐应明,史新,等. 海泡石对镉污染红壤的钝化修复效应研究. 环境科学学报, 2012, 32(6): 1465-1472 Sun Y.B., Xu Y.M., Shi X., et al. The effects of sepiolite on immobilization remediation of Cd contaminated red soil. Acta Scientiae Circumstantiae, 2012, 32(6): 1465-1472(in Chinese)
    [21] 宋和付, 陈安国, 夏畅斌. 膨润土吸附去除Zn2+、Cd2+的研究.材料保护, 2001, 34(9): 40-41 Song F.H., Chen A.G., Xia C.B., et al. Study on the adsorption of Zn2+,Cd2+ ions with activated bentonite. Journal of Materials Protection, 2001, 34(9): 40-41(in Chinese)
    [22] Stipp S. L., Hochella M. F., Parks G. A., et al. Cd2+ uptake by calcite, solid-state diffusion, and the formation of solid-solution: interface processes observed with near-surface sensitive techniques (XPS, LEED, and AES). Geochimca et Cosmochimca Acta, 1992,56(5):1941-1954
    [23] ITRC. Permeable Reactive Barriers: Lessons Learned/New Directions. PRB-4. Interstate Technology & Regulatory Council, Permeable Reactive Barriers Team, Washington D. C., 2005
    [24] 孙洪良. 复合改性膨润土对水中有机物和重金属的协同吸附研究. 杭州:浙江大学博士学位论文, 2010 Sun H.L. Study on simultaneous sorption of organic polluntants and heavy metals to bentonite modified by surfactant and organic ligands from water. Hangzhou: Doctoral Dissertation of Zhejiang University, 2010(in Chinese)
  • 加载中
计量
  • 文章访问数:  1762
  • HTML全文浏览数:  1209
  • PDF下载数:  709
  • 施引文献:  0
出版历程
  • 收稿日期:  2013-07-08
  • 刊出日期:  2014-05-29
曾婧滢, 秦迪岚, 毕军平, 罗岳平, 朱润良, 廖希谷, 张建新, 吕焕哲. 天然矿物组合材料渗透反应墙修复地下水镉污染[J]. 环境工程学报, 2014, 8(6): 2435-2442.
引用本文: 曾婧滢, 秦迪岚, 毕军平, 罗岳平, 朱润良, 廖希谷, 张建新, 吕焕哲. 天然矿物组合材料渗透反应墙修复地下水镉污染[J]. 环境工程学报, 2014, 8(6): 2435-2442.
Zeng Jingying, Qin Dilan, Bi Junping, Luo Yueping, Zhu Runliang, Liao Xigu, Zhang Jianxin, Lü Runliang. Remediation of cadmium contaminated ground-water using natural mineral combination materials based permeable reactive barrier[J]. Chinese Journal of Environmental Engineering, 2014, 8(6): 2435-2442.
Citation: Zeng Jingying, Qin Dilan, Bi Junping, Luo Yueping, Zhu Runliang, Liao Xigu, Zhang Jianxin, Lü Runliang. Remediation of cadmium contaminated ground-water using natural mineral combination materials based permeable reactive barrier[J]. Chinese Journal of Environmental Engineering, 2014, 8(6): 2435-2442.

天然矿物组合材料渗透反应墙修复地下水镉污染

  • 1.  湖南省环境监测中心站, 长沙 410014
  • 2.  国家环境保护重金属污染监测重点实验室, 长沙 410014
  • 3.  湘潭大学环境科学与工程系, 湘潭 411105
  • 4.  中国科学院广州地球化学研究所, 广州 510640
  • 5.  湖南省地质研究所, 长沙 410007
基金项目:

国土资源部公益性行业科研专项(201111016-1)

摘要: 实验模拟地下环境,以天然矿物材料石灰石、海泡石和膨润土作为可渗透反应墙(PRB)填充材料,采用正交实验法设计了16种可渗透反应器,研究了天然矿物组合材料组配对污染地下水模拟液中镉污染的修复效果、出水pH、有效孔隙度和渗透系数的影响,同时对机理进行了分析。实验结果显示,组合材料对镉去除率达99.8%以上,石灰石对处理效果贡献最大,增加石灰石用量,处理效果明显改善,当石灰石含量为10%及更高时,对含镉1.0 mg/L的污染地下水模拟液处理后镉浓度低于0.7 μg/L,达到地下水质量标准GB/T 14848-93规定的II类水质标准;石灰石用量的增加对渗透系数影响不大,但出水pH呈弱碱性(7

English Abstract

参考文献 (24)

返回顶部

目录

/

返回文章
返回