Adsorption of Cu(II), Cd(II), and Pb(II) from aqueous single metal solutions by sugarcane bagasse and mercerized sugarcane bagasse chemically modified with succinic anhydride
Introduction
Heavy metal ions are known to be toxic and carcinogenic to living organisms (Clement et al., 1995, MacCarthy et al., 1995). Their presence in the aquatic environment has been of great concern because of their toxicity and non biodegradable nature. Some metal ions are cumulative poisons, capable of being assimilated and stored in the tissues of organisms, causing noticeable adverse physiological effects (Gupta & Ali, 2000).
The removal of toxic metal ions from water is a very difficult task due to the high cost of treatment methods (Weng & Huang, 1994). There are various methods for the removal of toxic metal ions from aqueous solutions: reverse osmosis, ion exchange, precipitation, electrodialysis, adsorption, etc. Among these methods, adsorption is by far the most versatile and widely used for the removal of different pollutants (Gupta & Ali, 2004).
Brazil is the world leading producer of sugarcane for both the alcohol and the sugar industries. These industries produce a large amount of sugarcane bagasse. According to the last official survey from CONAB, an agency from the Brazilian Ministry of Agriculture, the national production of sugarcane in 2007/2008 was 527 million tons, the largest of all times. On average, 280 kg of sugarcane bagasse containing 50% moisture are produced by ton of sugarcane. In those industries, bagasse is burned in order to produce energy for sugar mills, but the leftovers are still significant (Karnitz Júnior et al., 2007). The remaining bagasse still continues to be a menace to the environment and a suitable utilization of this residue is an important target to be pursued (Sun, Sun, Zhao, & Sun, 2004). Sugarcane bagasse is constituted mainly of cellulose (40–50%), polyoses (25–30%), and lignin (20–25%) (Caraschi, Campana, & Curvelo, 1996).
Hassan and El-Wakil (2003) have reported the use of amidoximated bagasse (Am-B) for adsorption of some heavy metal ions such as Cu(II), Hg(II), Ni(II), Cr(III), and Pb(II) from aqueous solutions. Adsorption studies were performed at different pHs, contact times, metal ion concentration, and temperatures. The maximum milligrams of metal ions adsorbed per gram of AM-B were 672, 156, 137, and 47 for Hg2+, Cr3+, Cu2+, and Ni2+, respectively.
Nada and Hassan (2006) have recently reported the chemical modification of bagasse fibers with the aim to prepare lignocellulosic materials for removal of heavy metal ions from wastewater. Different reactions were used to modify bagasse fibers and to produce the following materials: oxy-bagasse, succinylated bagasse, and carboxymethylated bagasse. Adsorption studies were performed to evaluate the ability of these cation exchangers to remove heavy metal ions. The maximum milligrams of metal ions adsorbed per gram of oxy-bagasse, succinylated bagasse, and carboxymethylated bagasse were 233, 88, 394, and 200; 170, 113, 321, and 88; 392, 460, 504, and 465, for Cu2+, Ni2+, Cr3+, and Fe3+, respectively.
Karnitz Júnior et al. (2007) have recently reported the use of sugarcane bagasse modified with succinic anhydride (MSB 2) for removal of Cu(II), Cd(II) and Pb(II) from aqueous solutions. The authors have reported that the hydroxyl and phenolic groups in sugarcane bagasse could be easily converted to carboxylic groups by using succinic anhydride. Adsorption studies to determine the maximum adsorption capacity (Qmax) of MSB 2 towards each heavy metal were developed. The results were analyzed by Langmuir and Freundlich models. MSB 2 exhibited a maximum adsorption capacity of 114 mg/g for Cu2+, 196 mg/g for Cd2+ and 189 mg/g for Pb2+ according to Langmuir model.
Gurgel, Karnitz Júnior, Gil, and Gil (2008) reported the use of modified non- and mercerized cellulose with succinic anhydride for removal of Cu(II), Cd(II) and Pb(II) from aqueous solutions. The authors reported the effect of mercerization in the increase of the fibers specific surface area and in their reactivity. The mercerization makes the hydroxyl groups of the cellulose macromolecules more accessible and decreases the cellulose crystallinity index by 7%. Modified mercerized cellulose exhibited an increase in the mass percent gain and in the concentration of carboxylic functions in relation to modified non-mercerized cellulose by 68% and 2.8 mmol/g, respectively. Adsorption studies to determine the maximum adsorption capacity (Qmax) of modified celluloses for metals ions were developed. The results were analyzed by Langmuir model. Modified mercerized cellulose exhibited an increase in the adsorption maximum capacity of 30.4 mg/g for Cu2+, 86.0 mg/g for Cd2+ and 205.9 mg/g for Pb2+ in relation to modified non-mercerized cellulose.
This work describes the preparation and evaluation of two materials from sugarcane bagasse to adsorb heavy metal ions in aqueous solutions. The first material was prepared by modification of sugarcane bagasse with succinic anhydride (SCB) and the second was prepared by mercerization of sugarcane bagasse with an aqueous NaOH solution (20 wt%) followed by reaction with succinic anhydride (MMSCB). The adsorption studies of Cu2+, Cd2+ and Pb2+ from aqueous single metal ion solutions by SCB and MMSCB were developed at different times, pHs, and metal ion concentration.
Section snippets
Materials
Sugarcane bagasse, a waste material of sugar-alcohol industry, was collected from an alcohol factory at Ouro Preto, Brazil. Succinic Anhydride and Pyridine were purchased from VETEC (Brazil). CuSO4·5H2O, Pb(NO3)2, CdCl2·2.5H2O were purchased from SYNTH (Brazil). Pyridine was refluxed with NaOH overnight and distilled.
Sugarcane bagasse preparation
Integral sugarcane bagasse was first dried under sunlight. The fibers were manually broken into small pieces and subsequently dried at 90 °C in an oven for 24 h. Sugarcane bagasse
X-ray diffraction and FTIR analysis for SCB, MSCB and MMSCB
The treatment of lignocellulosic materials such as sisal, cotton linters and sugarcane bagasse with aqueous NaOH solution and the removal of lignin and polyoses together with the rearrangement of chain crystal packing from cellulose I in cellulose II have been reported by Ass, Ciacco, and Frollini (2006) and López et al. (2000), regarding position shifts and peak intensities in diffractrogram and FTIR spectra. Reactions such as the inclusion of alkali and water in cellulose and the splitting
Conclusions
The two alkaline treatments of sugarcane bagasse removed large amount of lignin and polyoses and also the amorphous cellulose fraction, converted cellulose I into cellulose II, decreased the crystallinity index and increased the separation of the cellulose chains. These modifications provided a higher degree of succinylation proven by higher mass percent gain and concentration of carboxylic functions exhibited by modified mercerized sugarcane bagasse MMSCB 1. MMSCB 2 exhibited higher adsorption
Acknowledgements
The authors thank the financial support from the following Brazilian Government Agencies: Fundação de Amparo à Pesquisa do Estado de Minas Gerais – FAPEMIG, Coordenação de Aperfeiçoamento de Pessoal de Nível Superior – CAPES. The authors are also grateful at Universidade Federal de Ouro Preto – UFOP.
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