4种人工湿地基质对马拉硫磷的吸附特性

苏凡凯, 于静洁, 周硕, 钟远, 孙力平, 王少坡. 4种人工湿地基质对马拉硫磷的吸附特性[J]. 环境工程学报, 2013, 7(8): 2849-2854.
引用本文: 苏凡凯, 于静洁, 周硕, 钟远, 孙力平, 王少坡. 4种人工湿地基质对马拉硫磷的吸附特性[J]. 环境工程学报, 2013, 7(8): 2849-2854.
Su Fankai, Yu Jingjie, Zhou Shuo, Zhong Yuan, Sun Liping, Wang Shaopo. Characteristics of malathion adsorption on four constructed wetland substrates[J]. Chinese Journal of Environmental Engineering, 2013, 7(8): 2849-2854.
Citation: Su Fankai, Yu Jingjie, Zhou Shuo, Zhong Yuan, Sun Liping, Wang Shaopo. Characteristics of malathion adsorption on four constructed wetland substrates[J]. Chinese Journal of Environmental Engineering, 2013, 7(8): 2849-2854.

4种人工湿地基质对马拉硫磷的吸附特性

  • 基金项目:

    国家水体污染控制与治理科技重大专项(2008ZX07209-006)

    国家自然科学基金资助项目(51108299)

    天津市自然科学基金资助项目(10JCYBJC05300)

  • 中图分类号: X592

Characteristics of malathion adsorption on four constructed wetland substrates

  • Fund Project:
  • 摘要: 通过基质对马拉硫磷的等温吸附和吸附动力学实验,研究天然土壤、煤渣、沸石、砾石对马拉硫磷的吸附特性,为人工湿地处理含马拉硫磷废水提供理论依据。结果表明:马拉硫磷浓度为2.25~90mg/L条件下,Langmuir和Freundlich方程均能较好地拟合4种基质对马拉硫磷的等温吸附过程,并且Freundlich方程的拟合效果要好于Langmuir方程。马拉硫磷的理论饱和吸附量大小依次为天然土壤(9.9304mg/g)>煤渣(1.6173mg/g)>沸石(0.6039mg/g)>砾石(0.3965mg/g)。4种基质对马拉硫磷的缓冲能力大小依次为天然土壤>煤渣>沸石>砾石,即当进水马拉硫磷浓度波动较大时,作为湿地基质天然土壤使人工湿地系统维持稳定出水水质的能力最强。马拉硫磷浓度为4.5mg/L条件下,吸附动力学模型Elovich方程能较好地拟合4种基质对马拉硫磷的吸附动力学特征,说明4种基质对马拉硫磷的吸附是表面吸附和内部扩散吸附共同作用的结果。因此,天然土壤和煤渣适宜作为处理含马拉硫磷废水的人工湿地基质。
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  • [1] 周芹.典型有机磷农药和多环芳烃的大气降解机理的理论研究.济南:山东大学博士学位论文,2011 Zhou Q. Theoretical study on the atmospheric degra-dation mechanism of typical organophosphorus pesticides and polycyclic aromatic hydrocarbons. Jinan: Doctoral Dissertation of Shandong University,2011(in Chinese)
    [2] Zhang Y. M., Pagilla K. Treatment of malathion pesticide wastewater with nanofiltration and photo-Fenton oxidation. Desalination, 2010,263(1-3):36-44
    [3] USEPA. Pesticides in Groundwater Database: 1988 Interim Report. Washington DC: Office of Pesticide Programs, 1988
    [4] Fadaei A., Dehghani M. H., Nasseri S., et al. Organophosphorous pesticides in surface water of Iran. Bulletin of Environmental Contamination and Toxicology, 2012,88(6):867-869
    [5] Gao J.J., Liu L.H., Liu X.R.,et al. The occurrence and spatial distribution of organophosphorous pesticides in Chinese surface water. Bull. Environ. Contam. Toxicol.,2009,82(2):223-229
    [6] USEPA.National Management Measures to Control Nonpoint Source Pollution from Agriculture. EPA 841-B-03-004:4-187-4-188,2003
    [7] Runes H. B., Jenkines J. J., Moore J. A. Treatment of atrazine in nursery irrigation runoff by a constructed wetland.Water Research,2003,37(3):539-550
    [8] 赵桂瑜.人工湿地除磷基质筛选及其吸附机理研究.上海:同济大学博士学位论文,2007 Zhao G. Y. Substances screening and its adsorption mechanism research of constructed wetland used for phosphorus removal.Shanghai: Doctoral Dissertation of Tongji University,2007(in Chinese)
    [9] 崔理华,朱夕珍,骆世明,等. 几种人工湿地基质磷的吸附特性研究.农业环境科学,2007,26(3):894-898 Cui L.H.,Zhu X.Z., Luo S.M., et al. The characteristics of phosphorous adsorption on different substances used in constructed wetland.Journal of Agro-Environment Science,2007,26(3):894-898(in Chinese)
    [10] 崔玉波,董婵,赵立辉,等.人工湿地填料吸附氮磷性能研究.吉林建筑工程学院学学报,2006,23(2):7-11 Cui Y.B.,Dong C.,Zhao L.H., et al. The performance study on adsorption of the filled material in constructed wetland.Journal of Jilin Architectural and Civil Engineering Institute,2006,23(2):7-11(in Chinese)
    [11] Vinay K., Ravi S. Singh, Prem N. Tiwari, et al. Removal of malathion from aqueous solutions and wastewater using fly ash. Water Resource and Protection, 2010,2(4):322-330
    [12] 李克斌,魏红,陈经涛,等.灭草松和莠去津在土壤中的竞争吸附.环境科学学报, 2006,26(7):1164-1171 Li K. B., Wei H., Chen J. T.,et al. Competitive adsorption between bentazone and atrazine in soils.Acta Scientiae Circumstantiae, 2006,26(7):1164-1171(in Chinese)
    [13] 莫汉宏.农药环境化学行为论文集.北京:中国科学技术出版社,1994.210-221
    [14] Zuhra Memon G., Bhanger I., Akhtar Mubeena,et al. Adsorption of methyl parathion pesticide from water using watermelon peels as a low cost adsorbent. Chemical Engineering Journal,2008,138(1-3):616-621
    [15] Rama Krishna K., Ligy Philip. Adsorption and desorption characteristics of lindane, carbofuran and methyl parathion on various Indian soils. Journal of Hazardous Materials, 2008,160(2-3):559-567
    [16] 赵俊岭. 农药西维因在土壤上的吸附行为机理研究.北京:北京交通大学硕士学位论文,2008 Zhao J.L. Sorption mechanisms of carbaryl onto soils and carbon adsorbent. Beijing: Master's Degree Thesis of Beijing Jiaotong University,2008(in Chinese)
    [17] 刘霄,黄岁樑,刘学功.3种人工湿地基质对磷的吸附特性.环境工程学报,2012,6(10):3367-3372 Liu X.,Huang S.L.,Liu X.G. Characteristics of phosphorous adsorption on three substrates used in constructed wetland. Chinese Journal of Environmental Engineering,2012,6(10):3367-3372(in Chinese)
    [18] 赵瑾瑾,贺小敏,冯伟亮,等.甲基对硫磷和西维因在粘土矿物表面的吸附解吸特性.应用化学,2010,27(1):112-116 Zhao J. J., He X.M., Feng W. L., et al. Sorption characteristics study of Parathion-methyl and carbaryl onto clay mineral surface. Chinese Journal of Applied Chemistry,2010,27(1):112-116(in Chinese)
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出版历程
  • 收稿日期:  2013-02-24
  • 刊出日期:  2013-08-12
苏凡凯, 于静洁, 周硕, 钟远, 孙力平, 王少坡. 4种人工湿地基质对马拉硫磷的吸附特性[J]. 环境工程学报, 2013, 7(8): 2849-2854.
引用本文: 苏凡凯, 于静洁, 周硕, 钟远, 孙力平, 王少坡. 4种人工湿地基质对马拉硫磷的吸附特性[J]. 环境工程学报, 2013, 7(8): 2849-2854.
Su Fankai, Yu Jingjie, Zhou Shuo, Zhong Yuan, Sun Liping, Wang Shaopo. Characteristics of malathion adsorption on four constructed wetland substrates[J]. Chinese Journal of Environmental Engineering, 2013, 7(8): 2849-2854.
Citation: Su Fankai, Yu Jingjie, Zhou Shuo, Zhong Yuan, Sun Liping, Wang Shaopo. Characteristics of malathion adsorption on four constructed wetland substrates[J]. Chinese Journal of Environmental Engineering, 2013, 7(8): 2849-2854.

4种人工湿地基质对马拉硫磷的吸附特性

  • 1.  天津城建大学环境与市政工程学院, 天津 300384
  • 2.  天津市水质科学与技术重点实验室, 天津 300384
  • 3.  中交水运规划设计院有限公司, 北京 100007
基金项目:

国家水体污染控制与治理科技重大专项(2008ZX07209-006)

国家自然科学基金资助项目(51108299)

天津市自然科学基金资助项目(10JCYBJC05300)

摘要: 通过基质对马拉硫磷的等温吸附和吸附动力学实验,研究天然土壤、煤渣、沸石、砾石对马拉硫磷的吸附特性,为人工湿地处理含马拉硫磷废水提供理论依据。结果表明:马拉硫磷浓度为2.25~90mg/L条件下,Langmuir和Freundlich方程均能较好地拟合4种基质对马拉硫磷的等温吸附过程,并且Freundlich方程的拟合效果要好于Langmuir方程。马拉硫磷的理论饱和吸附量大小依次为天然土壤(9.9304mg/g)>煤渣(1.6173mg/g)>沸石(0.6039mg/g)>砾石(0.3965mg/g)。4种基质对马拉硫磷的缓冲能力大小依次为天然土壤>煤渣>沸石>砾石,即当进水马拉硫磷浓度波动较大时,作为湿地基质天然土壤使人工湿地系统维持稳定出水水质的能力最强。马拉硫磷浓度为4.5mg/L条件下,吸附动力学模型Elovich方程能较好地拟合4种基质对马拉硫磷的吸附动力学特征,说明4种基质对马拉硫磷的吸附是表面吸附和内部扩散吸附共同作用的结果。因此,天然土壤和煤渣适宜作为处理含马拉硫磷废水的人工湿地基质。

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