Chemical Engineering Journal 158 (2010) 393–401
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Chemical Engineering Journal
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Adsorption of anionic dyes on chitosan grafted poly(alkyl methacrylate)s
Vinod Kumar Konaganti
a
, Ramanjaneyulu Kota
a
, Satish Patil
b
, Giridhar Madras
a,b,∗
a
Department of Chemical Engineering, Indian Institute of Science, Bangalore, Karnataka 560012, India
b
Solid State and Structural Chemistry Unit, Indian Institute of Science, Bangalore, Karnataka 560012, India
article info
Article history:
Received 16 November 2009
Received in revised form 3 January 2010
Accepted 4 January 2010
Keywords:
Adsorption
Kinetics
Chitosan
Chitosan grafting
Poly(alkyl methacrylate)s
abstract
Chitosan grafted poly(alkyl methacrylate)s (namely chitosan grafted poly(methyl methacrylate) (ChgP-
MMA), chitosan grafted poly(ethyl methacrylate) (ChgPEMA), chitosan grafted poly(butyl methacrylate)
(ChgPBMA) and chitosan grafted poly(hexyl methacrylate) (ChgPHMA)) were synthesized and charac-
terized by using FT-IR and
13
C NMR techniques. The adsorption batch experiments on these grafted
copolymers were conducted by using an anionic sulfonated dye, Orange-G. A pseudo-second-order kinetic
model was used to determine the kinetics of adsorption. The effect of grafting, effect of process variables
and the effect of different sulfonated anionic dyes (Orange-G, Congo Red, Remazol Brill Blue R and Methyl
Blue) on the adsorption kinetics was determined. The Langmuir and Freundlich models were used to fit
the adsorption isotherms and from the values of correlation coefficients (R
2
), it was observed that the
experimental data fits very well to the Langmuir model. The values of the maximum adsorption capacity
of the adsorbents follow the order: ChgPMMA > ChgPEMA > ChgPBMA > ChgPHMA > chitosan.
© 2010 Elsevier B.V. All rights reserved.
1. Introduction
Dye effluents discharged from textile and paper/pulp indus-
tries are major sources of aquatic pollution. Several methods such
as coagulation, biodegradation, adsorption, membrane separation,
ion-exchange, incineration, etc. have been reported for waste water
treatment. Among all these methods, adsorption is a both an effec-
tive and economical method for the removal of dyes from aqueous
solutions [1,2]. Even though the adsorption of dyes on to activated
carbon is effective, its widespread use has been limited because of
high cost and problems with its disposal [2].
Adsorption in presence of different biosorbent materials such as
agricultural wastes, bacterial biomass and biopolymers have been
reported in literature [3]. In particular, chitosan has proved to be an
effective biosorbent for removing the dyes from aqueous solutions
because of its non-toxicity, biocompatibility, biodegradability, anti-
bacterial property and high sorption capacity [4]. Chitosan and their
derivatives have a high affinity for adsorption towards reactive and
disperse dyes [5–7]. A detailed review on dye removal from aque-
ous solutions by adsorption using chitosan has been presented [1].
Chitosan is often grafted with polymers to improve its adsorp-
tion and mechanical properties. Jayakumar et al. have presented a
∗
Corresponding author at: Department of Chemical Engineering, Indian Institute
of Science, Bangalore, Karnataka 560012, India. Tel.: +91 80 22932321;
fax: +91 80 23600683.
E-mail addresses: giridhar@chemeng.iisc.ernet.in, giridharmadras@gmail.com
(G. Madras).
detailed review on graft copolymerized chitosan and their appli-
cations [8]. Chitosan has been grafted with poly(acrylic acid) [9],
poly(methacrylic acid) [10,11], poly(methyl methacrylate) [12] and
modified with montmorillonite [13], -cyclodextrin [14], fatty acid
glycidyl [15], and crosslinked with glutaraldehyde [16]. All these
materials have been successfully used for the adsorption of metal
ions and dyes.
However, the effect of the alkyl group substituent of the grafted
polymer on the adsorption kinetics has not been investigated. In the
present study, a series of chitosan grafted poly(alkyl methacrylate)s
has been synthesized and used for the adsorption of different types
of sulfonated anionic dyes. The present study also determines the
effect of process variables, grafting percentage and different dyes
on the adsorption kinetics.
2. Experimental
2.1. Materials
Chitosan (molecular weight of 300 kDa and 81% of degree
of deacetylation) was purchased from Sigma Aldrich (USA) and
used without any further purification. All the monomers methyl
methacrylate (MMA), ethyl methacrylate (EMA), n-butyl methacry-
late (BMA) and hexyl methacrylate (HMA) were purchased from
Sigma Aldrich (USA) and used after washing with 5% alkali solution
to remove phenolic inhibitor. Potassium persulfate from S. D. Fine
Chemicals (India) and ascorbic acid from Sisco research laboratories
(India) were used without further purification. Acetone and formic
acid (90%) were obtained from Merck (India). The dyes, Orange-G
1385-8947/$ – see front matter © 2010 Elsevier B.V. All rights reserved.
doi:10.1016/j.cej.2010.01.003