Journal of Hazardous Materials 168 (2009) 304–309
Contents lists available at ScienceDirect
Journal of Hazardous Materials
journal homepage: www.elsevier.com/locate/jhazmat
Removal of Basic Red 46 dye from aqueous solution by adsorption
onto Moroccan clay
A. Bennani Karim
a,b
, B. Mounir
a,∗
, M. Hachkar
a
, M. Bakasse
c
, A. Yaacoubi
b
a
The Team of Research Analysis, Checks and Environment, High School of Technology, University Cadi Ayyad, Dar Si Aissa Road, BP 89, Safi, Morocco
b
The Team Environmental and Experimental Methodology, Laboratory of Organic Applied Chemistry, Faculty of the Sciences Semlalia, BP 2390, Marrakech, Morocco
c
The Team of Analysis of the Microphones Polluting Organic, Faculty of the Sciences, University Chouaib Doukkali, BP 20, El Jadida, Morocco
article info
Article history:
Received 31 July 2008
Received in revised form 6 February 2009
Accepted 6 February 2009
Available online 20 February 2009
Keywords:
Basic Red
Moroccan clay
Adsorption
Isotherms
Kinetics
Thermodynamic parameters
abstract
In this study, Moroccan crude clay of Safi, which was characterized by X-ray diffraction, is used as adsor-
bent for the investigation of the adsorption kinetics, isotherms and thermodynamic parameters of the
Basic Red 46 (BR46) in aqueous solutions at various dye concentrations, adsorbent masses and pH val-
ues. The results showed that the adsorption capacity of the dye increased by initial dye concentration
and pH values. Two kinetic models (the pseudo-first-order and the pseudo-second-order) were used
to calculate the adsorption rate constants. The adsorption kinetics of the basic dye followed pseudo-
second-order model. The experimental data isotherms were analyzed using the Langmuir, Freundlich
and Dubinin–Radushkevish equations. The monolayer adsorption capacity for BR46 dye is 54mg/g of
crude clay. Nearly 20 min of contact time was found to be sufficient for the dye adsorption to reach equi-
librium. Thermodynamical parameters were also evaluated for the dye–adsorbent system and revealed
that the adsorption process is exothermic in nature.
© 2009 Elsevier B.V. All rights reserved.
1. Introduction
Dyes are synthetic aromatic compounds which are embodied
with various functional groups. They are widely used in textile,
leather, paper, plastic, and other industries. Some of these dyes may
degrade to produce carcinogens and toxic products [1]. Thus, the
removal of dyes from effluents is important for risk assessment.
Several physical or chemical processes are used to treat dye
laden wastewaters. These processes include flocculation, pre-
cipitation, ion exchange, membrane filtration, electrochemical
destruction, irradiation and ozonation. However, these processes
are costly and lead to generation of sludge or formation of by-
products [2]. Among the physical methods available, adsorption
process is one of the most efficient methods to remove dyes from
wastewater, especially if the adsorbent is inexpensive and readily
available [3]. Activated carbon is the most widely used adsorbent
for dye removal, but it is too expensive [4], consequently, numer-
ous low-cost alternative adsorbents have been proposed including:
peat [5], sepiolite [6], montmorillonite, chitosan and nanocompos-
ite [7], and pine sawdust [8]. Clays are mostly used as available
adsorbent and catalyst [9].
∗
Corresponding author at: Ecole Supérieure de Technologie, Université Cadi
Ayyad, BP 89, Safi, Morocco. Tel.: +212 61 28 93 66; fax: +212 24 62 91 24.
E-mail address: mounirbadia@yahoo.fr (B. Mounir).
In the present work, adsorption of Basic Red 46 (BR46) dye
onto Moroccan crude clay has been investigated and the obtained
experimental data were analyzed using adsorption isotherm mod-
els namely, Langmuir, Freundlich, and Dubinin–Radushkevich. The
effect of pH, adsorbent mass and initial dye concentration has been
studied. Kinetic experiments have been also conducted to deter-
mine the rate of BR46 adsorption onto clay.
2. Materials and methods
2.1. Materials
The basic dye used as adsorbate in the present study is C.I. Basic
Red 46 (Mr = 357.5), which was purchased from SDI textile company
(Safi, Morocco). The BR46 molecular structure is shown in Fig. 1. The
clay used in this study was ground from the natural basin of Safi and
sieved to 0.08–0.1 m size fraction. Then, it was dried at 105
◦
C for
24 h and used for further experiments.
The chemical composition of the adsorbent was determined by
using Philips X’ Cem X-ray fluorescence spectrometer (XRF). The
results are given in Table 1. XRD analyses of the powder sample
were performed using Siemens D-5000 X-ray diffractometer. The
physical properties (including BET, external surface area, total pore
volume and micropore volume, as well as average pore size distri-
bution) of crude clay were obtained by measuring their nitrogen
adsorption–desorption isotherms at -196
◦
C with the use of a sur-
0304-3894/$ – see front matter © 2009 Elsevier B.V. All rights reserved.
doi:10.1016/j.jhazmat.2009.02.028