Ethylenediamine grafted poly(glycidylmethacrylate-co-methylmethacrylate) adsorbent for removal of chromate anions

被引:97
作者
Bayramoglu, G [1 ]
Arica, MY [1 ]
机构
[1] Kirikkale Univ, Fac Sci, Biochem Proc & Biomed Res Lab, TR-71450 Kirikkale, Turkey
关键词
beads; adsorption; heavy metal removal; CrO42-; anions; kinetic characterization;
D O I
10.1016/j.seppur.2005.03.009
中图分类号
TQ [化学工业];
学科分类号
0817 ;
摘要
The removal of chromate anions (CrO42-) from aqueous solutions under different experimental conditions using cross-linked poly(glycidylmethacrylate-co-methylmethacrylate), poly(GMA-co-MMA), adsorbent was investigated in this study. The epoxy group containing adsorbent in the beads form was prepared from glycidylmethacrylate and methylmethacrylate via suspension polymerization. The epoxy groups of the poly (GMA-co-MMA) beads were used for grafting with ethylenediamine to prepare specific adsorbent (poly(GMA-co-MMA)-ED) for CrO42- anions removal from aqueous solutions. Adsorption equilibrium was achieved in approximately 120 min. The removal was favored at low pH, with a maximum adsorption at pH 2.0. Isotherm studies showed that CrO42- anions could be effectively removed by poly(GMA-co-MMA)-ED beads. The maximum adsorption capacities of the poly(GMA-co-MMA) and poly(GMA-co-MMA)-ED beads were 0.044 and 0.441 mmol CrO42- anions/g of dry adsorbents, respectively. The experimental data of the adsorption equilibrium from CrO42- anions aqueous solution correlated well with the Langmuir-Freundlich isotherm model. The experimental data were analyzed using the first- and the second-order kinetic models. The rate constants of adsorption for both kinetics models have been calculated. The second-order model provides the best correlation of the data. Desorption experiments show that the process of adsorption of CrO42- anions was reversible and the adsorbent was easily regenerated with 0.1 M NaOH up to 96% recovery. (C) 2005 Elsevier B.V. All rights reserved.
引用
收藏
页码:192 / 199
页数:8
相关论文
共 36 条
[1]  
[Anonymous], QUANTITATIVE ORGANIC
[2]   Utilisation of native, heat and acid-treated microalgae Chlamydomonas reinhardtii preparations for biosorption of Cr(VI) ions [J].
Arica, MY ;
Tüzün, I ;
Yalçin, E ;
Ince, Ö ;
Bayramoglu, G .
PROCESS BIOCHEMISTRY, 2005, 40 (07) :2351-2358
[3]   Biosorption of Hg2+, Cd2+, and Zn2+ by Ca-alginate and immobilized wood-rotting fungus Funalia trogii [J].
Arica, MY ;
Bayramoglu, G ;
Yilmaz, M ;
Bektas, S ;
Genç, Ö .
JOURNAL OF HAZARDOUS MATERIALS, 2004, 109 (1-3) :191-199
[4]  
BAJPAI J, 2004, COLLOID SURF A, V236, P8190
[5]   Dye-ligand immobilized IPNs membrane for removal heavy metal ions [J].
Bayramoglu, G ;
Yalçin, E ;
Genç, Ö ;
Arica, MY .
MACROMOLECULAR SYMPOSIA, 2003, 203 :219-224
[6]   Biosorption of heavy metal ions on immobilized white-rot fungus Trametes versicolor [J].
Bayramoglu, G ;
Bektas, S ;
Arica, MY .
JOURNAL OF HAZARDOUS MATERIALS, 2003, 101 (03) :285-300
[7]   Entrapment of Lentinus sajor-caju into Ca-alginate gel beads for removal of Cd(II) ions from aqueous solution:: preparation and biosorption kinetics analysis [J].
Bayramoglu, G ;
Denizli, A ;
Bektas, S ;
Arica, MY .
MICROCHEMICAL JOURNAL, 2002, 72 (01) :63-76
[8]   Synthesis of cation-exchange adsorbent for anchoring metal ions by modification of poly(glycidyl methacrylate) chains grafted onto polypropylene fabric [J].
Bondar, Y ;
Kim, HJ ;
Yoon, SH ;
Lim, YJ .
REACTIVE & FUNCTIONAL POLYMERS, 2004, 58 (01) :43-51
[9]   Mercury removal from water by ion exchange resins adsorption [J].
Chiarle, S ;
Ratto, M ;
Rovatti, M .
WATER RESEARCH, 2000, 34 (11) :2971-2978
[10]   Cork biomass as biosorbent for Cu(II), Zn(II) and Ni(II) [J].
Chubar, N ;
Carvalho, JR ;
Correia, MJN .
COLLOIDS AND SURFACES A-PHYSICOCHEMICAL AND ENGINEERING ASPECTS, 2003, 230 (1-3) :57-65