磁性硅藻土的制备及其性能

韩琳, 陈宋辉, 于鹏, 李溪, 赵吉, 徐炎华. 磁性硅藻土的制备及其性能[J]. 环境工程学报, 2016, 10(6): 2987-2991. doi: 10.12030/j.cjee.201501046
引用本文: 韩琳, 陈宋辉, 于鹏, 李溪, 赵吉, 徐炎华. 磁性硅藻土的制备及其性能[J]. 环境工程学报, 2016, 10(6): 2987-2991. doi: 10.12030/j.cjee.201501046
Han Lin, Chen Songhui, Yu Peng, Li Xi, Zhao Ji, Xu Yanhua. Preparation and performance of magnetic diatomite[J]. Chinese Journal of Environmental Engineering, 2016, 10(6): 2987-2991. doi: 10.12030/j.cjee.201501046
Citation: Han Lin, Chen Songhui, Yu Peng, Li Xi, Zhao Ji, Xu Yanhua. Preparation and performance of magnetic diatomite[J]. Chinese Journal of Environmental Engineering, 2016, 10(6): 2987-2991. doi: 10.12030/j.cjee.201501046

磁性硅藻土的制备及其性能

  • 基金项目:

    江苏省自然科学基金重点研究专项(BK2011016)

    江苏省环保科研课题项目(201004)

  • 中图分类号: X703

Preparation and performance of magnetic diatomite

  • Fund Project:
  • 摘要: 针对现有硅藻土吸附容量小和固液分离难的问题,采用共沉淀法制备2种磁改性硅藻土:Ⅰ和Ⅱ,通过扫描电镜(SEM)、比表面积测定(BET)、X射线衍射(XRD)等对制备的磁性硅藻土进行结构分析,并采用磁滞回线评估其磁性;考察了溶液pH、吸附剂用量和吸附时间对其吸附硝基苯的影响以及吸附饱和后的固液分离性能。结果表明:2种磁改性样品的饱和磁化强度分别为26.28 emu/g和4.8 emu/g,比表面积分别为39.242 m2/g和60.588 m2/g,为原土的1.3倍和2倍;对硝基苯的去除率分别达74.95%和95.2%,为原土的1.8倍和2.3倍;吸附饱和的磁改性样品在外加磁场作用下可迅速实现固液分离,且分离后2种磁改性样品溶液的悬浮物浓度分别为8.6 mg/L和9.8 mg/L。
  • 加载中
  • [1] 林俊雄. 硅藻土基吸附剂的制备、表征及其染料吸附特性研究. 杭州: 浙江大学博士学位论文, 2007 Lin Junxiong. Study on preparation, characterization and dyes adsorption properties of diatomite-based adsorbent. Hangzhou: Doctor Dissertation of Zhejiang University, 2007(in Chinese)
    [2] 刘洁, 赵东风. 硅藻土的研究现状及进展. 环境科学与管理, 2009, 34(5): 104-106 Liu Jie, Zhao Dongfeng. The present situation and development of diatomite. Environmental Science and Management, 2009, 34(5): 104-106(in Chinese)
    [3] Arik H. Synthesis of Si3N4 by the carbo-thermal reduction and nitridation of diatomite. Journal of the European Ceramic Society, 2003, 23(12): 2005-2014
    [4] Akin S., Schembre J. M., Bhat S. K., et al. Spontaneous imbibition characteristics of diatomite. Journal of Petroleum Science and Engineering, 2000, 25(3-4): 149-165
    [5] Hoffman B. T., Kovscek A. R. Displacement front stability of steam injection into high porosity diatomite rock. Journal of Petroleum Science and Engineering, 2005, 46(4): 253-266
    [6] Al-Ghouti M., Khraisheh M. A. M., Ahmad M. N. M., et al. Thermodynamic behaviour and the effect of temperature on the removal of dyes from aqueous solution using modified diatomite: A kinetic study. Journal of Colloid Interface Science, 2005, 287(1): 6-13
    [7] Gao Baojiao, Jiang Pengfei, An Fuqiang, et al. Studies on the surface modification of diatomite with polyethyleneimine and trapping effect of the modified diatomite for phenol. Applied Surface Science, 2005, 250(1-4): 273-279
    [8] 刘自莲, 李鹏, 施永生, 等. 硅藻土改性及其在废水处理中的应用研究现状. 工业用水与废水, 2010, 41(4): 5-8 Liu Zilian, Li Peng, Shi Yongsheng, et al. Research status of diatomite modification and its application in wastewater treatment. Industrial Water & Wastewater, 2010, 41(4): 5-8(in Chinese)
    [9] 赵浩, 于鹏, 徐炎华. 硅藻土改性及其对硝基苯模拟废水的吸附能力研究. 污染防治技术, 2013, 26(6): 14-18 Zhao Hao, Yu Peng, Xu Yanhua. Studies on adsorption capacity of nitrobenzene in simulated wastewater by modified diatomite. Pollution Control Technology, 2013, 26(6): 14-18(in Chinese)
    [10] Al-Degs Y., Khraisheh M. A. M., Tutunji M. F. Sorption of lead ions on diatomite and manganese oxides modified diatomite. Water Research, 2001, 35(15): 3724-3728
    [11] Shawabkeh R. A., Tutunji M. F. Experimental study and modeling of basic dye sorption by diatomaceous clay. Applied Clay Science, 2003, 24(1-2): 111-120
    [12] Aivalioti M., Papoulias P., Kousaiti A., et al. Adsorption of BTEX, MTBE and TAME on natural and modified diatomite. Journal of Hazardous Materials, 2012, 207-208: 117-127
    [13] Al-Ghouti M. A., Khraisheh M. A. M., Ahmad M. N., et al. Microcolumn studies of dye adsorption onto manganese oxides modified diatomite. Journal of Hazardous Materials, 2007, 146(1-2): 316-327
    [14] Aivalioti M., Vamvasakis I., Gidarakos E. BTEX and MTBE adsorption onto raw and thermally modified diatomite. Journal of Hazardous Materials, 2010, 178(1-3): 136-143
    [15] Huttenloch P., Roehl K. E., Czurda K. Sorption of nonpolar aromatic contaminants by chlorosilane surface modified natural minerals. Environmental Science & Technology, 2001, 35(21): 4260-4264
    [16] 李海燕, 黄延, 安立超. 含硝基苯类化合物废水处理技术研究. 工业水处理, 2006, 26(7): 40-43 Li Haiyan, Huang Yan, An Lichao. Study of treatment technology of wastewater containing nitrobenzene compounds. Industrial Water Treatment, 2006, 26(7): 40-43(in Chinese)
    [17] 杨明顺,解强,刑雯雯,等.铁系添加剂对煤基磁性活性炭性能的影响.中国矿业大学学报,2010,39(6): 897-901 Yang Mingshun, Xie Qiang, Xing Wenwen, et al. Effects of Fe-containing additives on performances of coal-based magnetic activated carbon. Journal of China University of Mining & Technology, 2010, 39(6): 897-901(in Chinese)
    [18] 吴东辉, 施新宇, 章忠秀, 等. 铁(Ⅱ)无机物热解制备γ-Fe2O3及其机理. 硅酸盐学报, 2006, 34(6): 699-702 Wu Donghui, Shi Xinyu, Zhang Zhongxiu, et al. Preparation of γ-Fe2O3 through pyrolysis of iron (II) inorganic compounds and its mechanism. Journal of the Chinese Ceramic Society, 2006, 34(6): 699-702(in Chinese)
  • 加载中
计量
  • 文章访问数:  3057
  • HTML全文浏览数:  2513
  • PDF下载数:  550
  • 施引文献:  0
出版历程
  • 收稿日期:  2015-04-01
  • 刊出日期:  2016-06-03
韩琳, 陈宋辉, 于鹏, 李溪, 赵吉, 徐炎华. 磁性硅藻土的制备及其性能[J]. 环境工程学报, 2016, 10(6): 2987-2991. doi: 10.12030/j.cjee.201501046
引用本文: 韩琳, 陈宋辉, 于鹏, 李溪, 赵吉, 徐炎华. 磁性硅藻土的制备及其性能[J]. 环境工程学报, 2016, 10(6): 2987-2991. doi: 10.12030/j.cjee.201501046
Han Lin, Chen Songhui, Yu Peng, Li Xi, Zhao Ji, Xu Yanhua. Preparation and performance of magnetic diatomite[J]. Chinese Journal of Environmental Engineering, 2016, 10(6): 2987-2991. doi: 10.12030/j.cjee.201501046
Citation: Han Lin, Chen Songhui, Yu Peng, Li Xi, Zhao Ji, Xu Yanhua. Preparation and performance of magnetic diatomite[J]. Chinese Journal of Environmental Engineering, 2016, 10(6): 2987-2991. doi: 10.12030/j.cjee.201501046

磁性硅藻土的制备及其性能

  • 1. 南京工业大学环境学院, 江苏省工业节水减排重点试验室, 南京 210009
  • 2. 南京工大环境科技有限公司, 南京 210009
基金项目:

江苏省自然科学基金重点研究专项(BK2011016)

江苏省环保科研课题项目(201004)

摘要: 针对现有硅藻土吸附容量小和固液分离难的问题,采用共沉淀法制备2种磁改性硅藻土:Ⅰ和Ⅱ,通过扫描电镜(SEM)、比表面积测定(BET)、X射线衍射(XRD)等对制备的磁性硅藻土进行结构分析,并采用磁滞回线评估其磁性;考察了溶液pH、吸附剂用量和吸附时间对其吸附硝基苯的影响以及吸附饱和后的固液分离性能。结果表明:2种磁改性样品的饱和磁化强度分别为26.28 emu/g和4.8 emu/g,比表面积分别为39.242 m2/g和60.588 m2/g,为原土的1.3倍和2倍;对硝基苯的去除率分别达74.95%和95.2%,为原土的1.8倍和2.3倍;吸附饱和的磁改性样品在外加磁场作用下可迅速实现固液分离,且分离后2种磁改性样品溶液的悬浮物浓度分别为8.6 mg/L和9.8 mg/L。

English Abstract

参考文献 (18)

返回顶部

目录

/

返回文章
返回