Simultaneous removal of Cr(VI) and Amido black 10B (AB10B) from aqueous solutions using quaternized chitosan coated bentonite
Introduction
Dyes are among the most commonly used pollutants which appear in various industries including dyestuff, textile, leather, and paper. A large number of dyes are azo compounds that are linked by an azo bridge. It was important to remove these dyes from water based on an environmental point of view because these dyes can be highly toxic to aquatic systems even at very low concentrations. Heavy metals are another hazardous pollutant commonly found in the effluents from several industries such as electronics assembly and fabrication, battery manu- facturing, paper and pulp industries, metal fabrication, and mining activities. Adsorption is considered as an economical method for improving water quality and can be used to remove different types of pollutants, especially dyes and heavy metals. At present, much attention has been paid to investigate the removal of dyes or heavy metals from single-component solutions [1], [2], [3], [4], [5]. Various adsorbents have been developed and applied, and they include activated carbons, natural and synthetic polymers, clays, zeolites, biomasses, agricultural and industrial by-products [6], [7], [8], [9], [10], [11], [12], [13]. However, heavy metals and dyes often existed together in the practical industrial effluents. A limited emphasis has been given to the study of multi-component systems. For example, R. Tovar-Gómez et al. reported the synergic adsorption in the simultaneous removal of acid blue 25 and heavy metals (Zn2+, Ni2+ and Cd2+) using a Ca(PO3)2-modified carbon [14]. N.P. Jović-Jovičić et al. investigated the simultaneous adsorption of Pb2+ and reactive dye-RB5 on the modified bentonites with hexadecyltrimethylammonium (HDTMA+) and quaternary alkyl ammonium cations (QAACs) [15]. Visa et al. studied the simultaneous removal of methylene blue and Cu2+, Ni2+ and Cd2+ in multi-component systems using fly ash modified with NaOH [16].
Bentonite is a clay mineral consisting of two tetrahedral sheets with Si in the cationic sites sandwiching an octahedral Al sheet. The partial substitution of Al3+ for the tetrahedral Si4+ and Mg2+ makes the layers negatively charged. Bentonite almost has no adsorption for anionic pollutants due to its negatively charged sheets. Therefore, bentonite, as an adsorbent, was often modified to broaden the application scope. Bentonite may be neutralized by exchangeable cations such as Ni, Co, Zn [17], cationic surfactants [15], and polymers [18], [19]. However, some cationic substances are difficult to degrade in nature and may be toxic to humans and the environment. Therefore, the use of natural cationic substances such as chitosan has generated increasing interest [20], [21]. However, chitosan has several disadvantages including easy agglomeration, poor mech- anical strength, and its solubility in dilute acids, thus the broad application of chitosan was limited to some degree.
Quaternized chitosan is a cationic polymer which is the quaternized derivative of chitosan. It contains multiple cationic charges and has good solubility in water. Based on its properties of biodegradability, biocompatibility, antimicrobial effects, good film formation, and high positive charge, quaternized chitosan has been applied in the preparation of composite films [22], [23], adsorbent material [24], and nanocomposites [25], [26]. In our previous work, it was found that quatenized chitosan/bentonite composite showed a potential for the removal of anionic pollutants [27]. In addition, Wang et al. [28] demonstrated that modification of montmorillonite with quater- nized chitosan could enhance the antimicrobial activity of montmorillonite in a weak acidic or weak basic medium.
In the present study, the modification of bentnoite was achieved by coating quaternized chitosan on bentonite. As heavy metal ion (target pollutant), Cr(VI), a highly toxic pollutant causing liver damage, pulmonary congestions and severe diarrhea, usually exist in many dyeing effluents discharged from leather tanning and dyestuff industries [29]. Chromium exists in the environment in the trivalent state or in the hexavalent state such as Cr (VI) anions: HCrO4−, CrO42−and Cr2O72−. Amido Black 10B (AB10B) was chosen as an azo dye molecule because it has been established that this dye has very high toxicity, and can damages the respiratory system of humans and also causes skin and eye irritations [30]. Moreover, since AB10B can be considered a typical anionic dye and Cr(VI) usually coexists in dyeing effluents, AB10B and Cr(VI) have been selected as target pollutants. The objective of this study is to coat quaternized chitosan on bentonite in order to increase or strengthen the interactions between the anionic pollutants (heavy metal and dye) and positively charged quaternized chitosan. The characterization of the composite material was investigated using FTIR and XRD techniques. The adsorption evaluation of Cr(VI) and Amido Black 10B was done by a batch method. Major adsorption factors including pH, adsorbent dosage, contact time, and initial pollutants’ concentrations as well as the interaction between Cr(VI) and Amido Black 10B were determined. In order to study the simultaneous removal of Cr(VI) and Amido Black 10B (synergetic or antagonistic), the isotherm and kinetic experiments in single and binary solutions (i.e., dye–metal ion) were also carried out.
Section snippets
Materials
Chitosan [weight-average molecular weight (MW) = 100,000 Da, degree of deacetylation (dd) = 90%] was purchased from the Sinopharm Group Chemical Reagent Limited Company (China) and used in the synthesis of quaternized chitosan. Quaternized chitosan, N-2-hydroxy- propyl trimethyl ammonium chloride chitosan was prepared according to our previous literature [27]. Bentonite powder with a particle size of 200-mesh was acquired from the chemical factory of Shentai, Xinyang, Henan, China. Amido black 10B
Characterization of quaternized chitosan coated bentonite
The XRD patterns of the composites with various quaternized chitosan/bentonite mass ratio were shown in Fig. 1. The XRD pattern of bentonite presented a typical reflection of mon- tmorillonite (d001) at 6.56°. It is obvious that the d001 diffraction peak in the quaternized chitosan coated bentonite with this ratio being 0.5 was shift to a lower angle, suggesting that the interlayer spacing of bentonite was expanded due to the intercalation of crosslinked quaternized chitosan into the interlayer
Conclusion
In this study, the quaternized chitosan coated bentonite was used for the simultaneous adsorption of Cr(VI) and AB10B from binary solution. The antagonism adsorption was observed between AB10B and Cr(VI) in binary solution. Equilibrium isotherm, kinetic and thermodynamic studies were also investigated. Both Cr(VI) and AB10B agreed well to Langmuir for both single and binary systems. The adsorption capacity (mg/g) of the modified bentonite was greater significantly for AB10B than the one for
References (35)
- et al.
J. Biol. Macromol.
(2015) - et al.
Appl. Clay Sci.
(2016) - et al.
Appl. Clay Sci.
(2015) - et al.
J. Environ. Chem. Eng.
(2016) - et al.
Appl. Clay. Sci.
(2016) - et al.
Bioresour. Technol.
(2008) - et al.
Bioresour. Technol.
(2008) - et al.
Int. J. Chem. Eng.
(2008) - et al.
Desalination
(2008) - et al.
Chem. Eng. J.
(2011)
Fresenius Environ. Bull.
Spectrochim. Acta A: Mol. Biomol. Sp.
Spectrochim. Acta A: Mol. Biomol. Sp.
J. Hazard Mater.
J. Contam. Hydrol.
Appl. Surf. Sci.
Dyes Pigm.
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