Carbohydrate Polymers 101 (2014) 684–691
Contents lists available at ScienceDirect
Carbohydrate Polymers
jo u r n al homep age: www.elsevier.com/locate/carbpol
Adsorptional removal of methylene blue by guar gum–cerium (IV)
tungstate hybrid cationic exchanger
V.K. Gupta
a,∗
, Deepak Pathania
b
, Pardeep Singh
b
, Amit Kumar
b
, B.S. Rathore
b
a
Department of Chemistry, Indian Institute of Technology, Roorkee 247667, India
b
School of Chemistry, Shoolini University, Solan 173212, Himachal Pradesh, India
a r t i c l e i n f o
Article history:
Received 15 August 2013
Received in revised form
21 September 2013
Accepted 27 September 2013
Available online 5 October 2013
Keywords:
Hybrid ion exchanger
Characterization
Methylene blue
Adsorption
Kinetics
a b s t r a c t
Guar gum–cerium (IV) tungstate nanocomposite (GG/CTNC) cationic exchanger was synthesized using
simple sol gel method. The GG/CTNC was characterized using X-ray diffraction (XRD), Fourier trans-
mission infrared spectroscopy (FTIR), scanning electron microscopy (SEM) and energy dispersive X-ray
spectrophotometer (EDX). The XRD studies confirmed amorphous and fibrous in nature of GG/CTNC.
The high percentage of oxygen in the nanocomposite material confirmed the functionality tungstate
(WO
4
-
). The ion exchange capacity of GG/CTNC for Na
+
ion was observed to be 1.30 mequiv g
-1
. The
hybrid exchanger was used as potential adsorbent for the removal of methylene blue (MB) from aque-
ous system. The correlation coefficients value indicated a good fit of monolayer Langmuir model to the
adsorption of methylene blue onto GG/CTNC. The adsorption kinetic study revealed that the adsorption
process followed the pseudo second order kinetic. The Gibbs free energy (G) values confirmed the
spontaneous nature of adsorption process.
© 2013 Elsevier Ltd. All rights reserved.
1. Introduction
The fast industrial development throughout world has sig-
nificantly increased the production of wastewater from various
industries such as, textile, paper, paint, and dyestuffs consume;
as a consequence toxic synthetic dyes are discharged into water
bodies. The discharged dyes degrade the water quality and may
cause adverse effect on human health due to toxic, mutagenic
and carcinogenic nature (Gupta & Ali, 2008; Gupta, Agarwal, &
Saleh, 2011; Gupta, Jain, & Varshney, 2007; Gupta, Mittal, Malviya,
& Mittal, 2009; Gupta, Rastogi, & Nayak, 2010; Gupta, Pathania,
Agarwal, & Singh, 2012; Mittal, Gupta, Malviya, & Mittal, 2008;
Mittal, Mittal, Malviya, Kaur, & Gupta, 2010). The synthetic dyes
are difficult to treat, since these are resistant to biological oxi-
dation/reduction, and stable to oxidizing agents. The application
of conventional methods like coagulation, flocculation, precipita-
tion, membrane separation, solvent extraction and adsorption, does
not treat industrial dye-effluent efficiently (Vilhera, Goncalves, &
Mota, 2004). In practice, no single process provides adequate treat-
ment and combination of different process has been often used to
improve the water quality in most greener and economic way. It
is now well recognized that bio-adsorbent are gaining importance
as effective and economic methods for wastewater remediation.
∗
Corresponding author. Fax: +91 1332273560.
E-mail addresses: vinodfcy@gmail.com, vinodfcy@iitr.ernet.in (V.K. Gupta),
dpathania74@gmail.com (D. Pathania).
A large number of non-conventional bio-adsorbents such as fun-
gal or bacterial biomass or biopolymers have been employed to
remove toxic metals and dyes from aqueous phase (Constantin
et al., 2013; Zhao, Zeng, Li, et al., 2012a; Zhao, Zeng, Hu, et al.,
2012b). The bio-adsorbent are low-cost, harmless and abundantly
available (Constantin et al., 2013; Yang et al., 2012). However,
lower stability, difficulty in separation from aqueous phase and low
recovery after desorption were the major limitations for large scale
applicability of bio-absorbents (Gupta et al., 2011, 2012).
Organic–inorganic nanocomposite materials are of importance
because of their multifunctionality owing to a combination of dif-
ferent compounds incorporated. Recently, TiO
2
, BiOCl, Fe
2
O
3
, CuS
and ZnO based bio-nanocomposites have been used for dyes and
metal removal from wastewater (Dong, Sun, Min, Wu, & Lee, 2012;
Gupta et al., 2012; Huang & Chen, 2009; Virkutyte, Jegatheesan,
& Varma, 2012). Nowadays, bio-material based nanocomposites
have drawn considerable attention because of their low-cost, easy
processability, high-volume application, renewable nature and
possibility of recycling. There are several research efforts reporting
the bio-composite with carbon nanotubes, lignin and lumiscent CdS
(Nevarez et al., 2011; Park & Kadla, 2012; Yang et al., 2012). Guar
is a naturally occurring polysaccharide extracted from the beans of
the guar gum plant. It is used as environmental-friendly thickener
to control visco-elasticity in food, personal care and oil recovery
industries. Cerium (IV) derivates represent inorganic ion exchang-
ers of tetravalent metal acid salts class. It has shown excellent
adsorption ability for heavy metal due to its high selectivity, high
thermal stability and absolute insolubility in water (Semischenko,
0144-8617/$ – see front matter © 2013 Elsevier Ltd. All rights reserved.
http://dx.doi.org/10.1016/j.carbpol.2013.09.092