玻璃抛光废渣理化特性研究

程俊华, 张健, 陈刚, 吕文晏. 玻璃抛光废渣理化特性研究[J]. 环境工程学报, 2013, 7(5): 1929-1932.
引用本文: 程俊华, 张健, 陈刚, 吕文晏. 玻璃抛光废渣理化特性研究[J]. 环境工程学报, 2013, 7(5): 1929-1932.
Cheng Junhua, Zhang Jian, Chen Gang, Lü Wenyan. Study on physical and chemical characteristics of slag polished from glass article[J]. Chinese Journal of Environmental Engineering, 2013, 7(5): 1929-1932.
Citation: Cheng Junhua, Zhang Jian, Chen Gang, Lü Wenyan. Study on physical and chemical characteristics of slag polished from glass article[J]. Chinese Journal of Environmental Engineering, 2013, 7(5): 1929-1932.

玻璃抛光废渣理化特性研究

  • 基金项目:

    江苏省科技支撑计划-社会发展项目(BE2010619)

    江苏省新型环保重点实验室开放课题基金资助项目(AE201110)

  • 中图分类号: X705

Study on physical and chemical characteristics of slag polished from glass article

  • Fund Project:
  • 摘要: 为处置和利用一种玻璃抛光废渣,用XRF、ICP、XRD、SEM、灰熔点炉、粒度分析和浸出毒性等实验手段对其化学成分、浸出毒性、颗粒径和比表面积等理化性质进行了系统研究。结果表明,玻璃抛光废渣虽然主体是 Si、Al、Fe、K、Na、Ca和Mg的硅酸盐,但含一定量的Pb、Ba、Cr、Mn、Zn、V、Cu和As等重金属元素,80%的粒径小于15 μm,平均粒径为6.31 μm,比表面积为480 m2/g,是一种细粉状浸出毒性较高的有害固废;烧结能有效地固封和固溶其中的重金属,可作为控制其污染和处置利用的有效措施。
  • [1] Zufiaurre R., Oliver A., Chamorro P. Speciation of metals in sewage sludge for agricultural uses. Analyst, 1998, 123(2): 255-259
    [2] 刘清,王子健,汤鸿宵.重金属形态与生物毒性及其生物有效性关系的研究进展.环境科学, 1996,17(1):89-92 Liu Qing, Wang Zijian, Tang Hongxiao. Research progress in heavy metal speciation and toxicity and bioavailability of heavy metals. Environmental Science, 1996, 17(1): 89-92 (in Chinese)
    [3] Richer U., Birnbaum L. Detailed investigations of filter ash from municipal solid waste incineration. Waste Manage Res, 1998,16(2):190-197
    [4] Wiles C. C. Municipal solid waste combustion ash: State of the knowledge.Journal of Hazardous Materials,1996,47(1-3):325-344
    [5] 中国国家标准局.GB5086.2-1997固体废物浸出毒性的浸出方法.北京:中国标准出版社,1997
    [6] 中国国家标准局.GB/T219-2008煤灰熔融性的测定方法.北京:中国标准出版社,2008
    [7] Tay J. H., Goh A. T. C. Engineering properties of incinerator residue.J. Environ. Eng. ASCE, 1991,117(2): 224-235
    [8] Chiou Ingjia, Wang Kuensheng, Chen Chingho, et al. Light weight aggregate made from sewage sludge and incinerated ash.Waste Management, 2006, 26(12): 1453-1461
    [9] 中国国家标准局.GBl5618-1995土壤环境质量标准.北京:中国标准出版社,1995
    [10] Wang Kuensheng, Sun Changjung, Ye Chungchi. The thermotreatment of MSW incinerator fly ash for use as an aggregate: A study of the characteristics of size-fractioning. Resour Conserv Recycl, 2002, 35(3): 177-190
    [11] Yin C. Y., Matmud H., Shaaban M. Stabilization/solidification of lead-contaminated soil using cement and rice husk ash. J. Hazard. Mater, 2006, 137(3): 1758-1764
    [12] Collivignarelli C., Sorlini S. Reuse of municipal solid wastes incineration fly ashes in concrete mixtures. Waste Manage, 2002, 22(8):909-912
    [13] 罗上庚,杨建文,朱鑫璋.人造岩石固化包容婀系核素废物.化学学报,2000,58(12):1608-1614 Luo Shanggen, Yang Jianwen, Zhu Xinzhang. Synroc solidfication of actinide wastes. Acta Chim. Sinica,2000, 58 (12):1608-1614 (in Chinese)
    [14] Young Jun Park, Jong Heo. Vitrification of fly ash from municipal solid waste incinerator.J. of Hazard Mater., 2002, B91:83-93
    [15] 姜永海,席北斗,李秀金,等.垃圾焚烧飞灰熔融固化处理过程特性分析.环境科学, 2005,26(3):176-179 Jiang Yonghai, Xi Beidou, Li Xiujin, et al. Characteristics of melting and solidification process of fly ash from refuse incinerator.Environmental Science, 2005, 26(3):176-179 (in Chinese)
    [16] Camobreco V. J., Richards B. K., Steenhuis T.S., et al. Movement of heavy metals through undisturbed and homogenized soil columns. Soil Science, 1996, 161(6):740-750
    [17] Malviya R., Chaudhary R. Factors affecting hazardous waste solidification/stabilization: A review. J. of Hazard. Mater., 2006, 137(1):267-276
    [18] Anstice D. J., Page C. L., Page M. M. The pore solution phase of carbonated cement paste.Cem. Concr. Res., 2005, 35(2):377-383
    [19] 田书磊,王琪,汪群慧,等.垃圾焚烧飞灰熔融过程中重金属固化特性.哈尔滨工业大学学报, 2008,40 (10):1576-1580 Ting Shulei, Wang Qi, Wang Qunhui, et al. Characterics of heavy metals during melting and solidification of MSWI fly ash.Journal of Harbin Institute of Technology, 2008, 40 (10):1576-1580 (in Chinese)
    [20] 李润东,池涌,王雷,等.城市垃圾焚烧飞灰熔融动力学研究.浙江大学学报(工学版), 2002,36(5):498-503 Li Rundong, Chi Yong, Wang Lei,et al. Kinetic study of MSW incineration fly ash melting by DSC-DTA. Journal of Zhejiang University (Engineering Science), 2002, 36(5):498-503 (in Chinese)
  • 加载中
计量
  • 文章访问数:  2025
  • HTML全文浏览数:  1123
  • PDF下载数:  763
  • 施引文献:  0
出版历程
  • 收稿日期:  2012-04-05
  • 刊出日期:  2013-05-22
程俊华, 张健, 陈刚, 吕文晏. 玻璃抛光废渣理化特性研究[J]. 环境工程学报, 2013, 7(5): 1929-1932.
引用本文: 程俊华, 张健, 陈刚, 吕文晏. 玻璃抛光废渣理化特性研究[J]. 环境工程学报, 2013, 7(5): 1929-1932.
Cheng Junhua, Zhang Jian, Chen Gang, Lü Wenyan. Study on physical and chemical characteristics of slag polished from glass article[J]. Chinese Journal of Environmental Engineering, 2013, 7(5): 1929-1932.
Citation: Cheng Junhua, Zhang Jian, Chen Gang, Lü Wenyan. Study on physical and chemical characteristics of slag polished from glass article[J]. Chinese Journal of Environmental Engineering, 2013, 7(5): 1929-1932.

玻璃抛光废渣理化特性研究

  • 1. 盐城工学院材料工程学院,盐城 224051
  • 2. 南京环务资源再生科技有限公司,南京 210098
  • 3. 南京航天航空大学材料科学与技术学院,南京 211100
基金项目:

江苏省科技支撑计划-社会发展项目(BE2010619)

江苏省新型环保重点实验室开放课题基金资助项目(AE201110)

摘要: 为处置和利用一种玻璃抛光废渣,用XRF、ICP、XRD、SEM、灰熔点炉、粒度分析和浸出毒性等实验手段对其化学成分、浸出毒性、颗粒径和比表面积等理化性质进行了系统研究。结果表明,玻璃抛光废渣虽然主体是 Si、Al、Fe、K、Na、Ca和Mg的硅酸盐,但含一定量的Pb、Ba、Cr、Mn、Zn、V、Cu和As等重金属元素,80%的粒径小于15 μm,平均粒径为6.31 μm,比表面积为480 m2/g,是一种细粉状浸出毒性较高的有害固废;烧结能有效地固封和固溶其中的重金属,可作为控制其污染和处置利用的有效措施。

English Abstract

参考文献 (20)

返回顶部

目录

/

返回文章
返回