Removal of Cu2+ and Cd2+ from Aqueous Solution by Bentonite Clay Modified with Binary Mixture of Goethite and Humic Acid

被引:1
作者
B. I. Olu-Owolabi
D. B. Popoola
E. I. Unuabonah
机构
[1] University of Ibadan,Department of Chemistry
[2] Redeemer’s University,Department of Chemical Sciences
[3] The University of the Witwatersrand,DST/NRF Centre of Excellence in Strong Materials
来源
Water, Air, & Soil Pollution | 2010年 / 211卷
关键词
Bentonite; Cation exchange capacity; Adsorption; Goethite; Humic acid; Copper; Cadmium;
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中图分类号
学科分类号
摘要
Pre-modification of bentonite clay with goethite, humic acid, and a binary mixture of goethite and humic acid reagents increased its cation exchange capacity from 95 to 105.32, 120.4, and 125.8 meq/100 g of bentonite clay, respectively. The effective pre-modification of bentonite clay with goethite, humic acid, and goethite–humic acid reagents was confirmed from their Fourier transform infrared spectra which suggested that modification was effective on the AlAlOH and Si–O sites for goethite and humic acid modification and AlAlOH for goethite–humic acid modification. The presence of 0.001 M NaNO3 electrolyte increased the adsorption capacity of bentonite clay. Temperature was observed to favor the adsorption of Cu2+ and Cd2+ onto both the raw and modified bentonite clay samples. The goethite–humic acid-modified bentonite gave the best adsorption capacity of ≈10 and 16 mg/g at 30 and 50°C, respectively, for both metal ions. The inner sphere complexation mechanism was suggested for the adsorption of both metal ions onto the modified adsorbents. Modifying bentonite clay with a binary mixture of goethite and humic acid reduced the selectivity of bentonite clay for either Cu2+ or Cd2+. Preadsorbed goethite and humic acid on bentonite clay will further reduce the mobility of heavy metal ions in soils and in aquatic environments.
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页码:459 / 474
页数:15
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[11]  
Al-Qunaibit MH(2007)Modelling the adsorption of Cd (II), Cu (II), Ni (II), Pb (II) and Zn (II) onto fithian illite Journal of Colloid and Interface Science 67 1378-1387
[12]  
Mekhemer WK(2003)Sorption–desorption of lead (II) and mercury (II) by model associations of soil colloids Soil Science Society of America Journal 3 281-288
[13]  
Zaghloul AA(2008)Kinetic and thermodynamic study of the adsorption of Pb (II) from aqueous solution to the natural and treated bentonite International Journal of Physical Sciences 69 1675-1686
[14]  
Arpa C(2005)Sorption of Cu and Pb to kaolinite–fulvic acid colloids: assessment of sorbent interactions Geochimica et Cosmochimica Acta 25 16-26
[15]  
Say R(1974)Anion adsorption by goethite and gibbsite II. Desorption of anions from hydrous oxide surfaces Journal of Soil Science 32 232-244
[16]  
Satiroghu N(2006)Modeling of cadmium(II) adsorption on kaolinite-based clays in the absence and presence of humic acid Applied Clay Science 210 248-256
[17]  
Bektas S(2007)Removal of Pb(II) from aqueous solutions by using clinoptilolite and bentonite as adsorbents Desalination 7 751-761
[18]  
Yürüm Y(1976)An evaluation of the cation exchange capacity measurements for soils in the tropics Communications in Soil Science and Plant Analysis 125 183-189
[19]  
Genc Ö(2005)Adsorption of zinc from aqueous solutions to bentonite J Hazard Mater 44 1701-1708
[20]  
Bordas F(1980)Sorption of metals on humic acid Geochimica et Cosmochimica Acta 40 796-799