Journal of the Taiwan Institute of Chemical Engineers
Decolorization and mineralization of an azo reactive dye using loaded nano-photocatalysts on spacer fabric: Kinetic study and operational factors
Introduction
The discharge of textile wastewater containing various organic and mineral pollutants such as dyes and pigments into natural streams and rivers causes serious environmental problems. In fact, most of the dyes owing to their conjugated aromatic compounds and complicated chemical structure are toxic to the aquatic living organisms [1], [2], [3], [4], [5].
Among the broad range of the dyes used in textile industry, reactive dyes due to their favorable characteristics such as low energy consumption in the dyeing process, color brightness and water fastness, have found extensive application and they constitute almost 50% of the annual worldwide production of the dyes [6].
Some reactive dyes, such as RBB which are composed of one or more azo bonds (NN) and aromatic rings are categorized as xenobiotic compounds. Additionally, because the fixation efficiency of azo dyes is estimated to fall in the range of 60% to 90%, their loss in the dyeing process causes environmental concerns [7], [8], [9].
The conventional methods for wastewater decolorization such as chemical, physical or biological methods only transform dyes from aqueous to another phase, which consequently results in secondary pollution [10], [11], [12], [13], [14], [15], [16], [17]. Therefore, post-treatments of the solid wastes, which are costly operations, are required [18], [19].
Currently, advanced oxidation processes (AOPs) have been developed as alternative methods for decolorization of dyes and other contaminated wastewaters. The main purpose of AOPs is to transfer all organic compounds to water, carbon dioxide and mineral acids [20]. Among different methods of AOPs, heterogeneous photocatalytic processes which use metal oxide semiconductor (MOS) nanoparticles such as TiO2 and ZnO are considered as the most effective approach in degrading and mineralizing organic compounds in wastewater [21]. The fundamental of this technique is based on the irradiation of ultraviolet (UV) light on MOS to produce reactive species such as hydroxyl radical (OH•) which oxidize a broad range of organic pollutants non-selectively [22], [23].
Although TiO2 is the most frequently used photocatalyst for a wide range of organic compounds, it exhibits some disadvantages [24], [25]. Among other semiconductors, ZnO represents an apt alternative candidate owing to the similarity of its photo-degradation mechanism to TiO2. Furthermore, it has been substantiated by some reports that ZnO is more efficient than TiO2 under certain conditions whose reason might be attributed to its higher quantum efficiency [26]. Photocatalytic processes incorporating semiconductor nanoparticles involve two typical approaches including suspension of the nanoparticles in solution and immobilization of the nanoparticles on surface. Amidst those, the immobilization method is preferred, because the catalyst separation and recycling from the treated wastewater prior to discharge are eliminated [27], [28].
There has been some reports on the immobilization of nano-photocatalysts onto solid materials such as glass wool, glass beads, glass reactors, microporous cellulosic membranes, ceramic membranes, monoliths, zeolites, and stainless steel [29]. However, the immobilization of nanoparticles on 3-dimensional polyethylene terephthalate fabrics (spacer fabrics) for photocatalytic processes has not been reported yet.
Spacer fabrics can be defined as complex 3-dimensional constructions composed of two separated layers of fabric which are connected with spacer yarns for whose production weaving and knitting technologies are generally required. The 3-dimensional structures of these fabrics make them markedly different from their conventional counterparts. Owing to the low possibility of physical or chemical absorption of the reactive dyes on polyethylene terephthalate (PET), spacer fabrics made of PET were selected in the current study. Furthermore, it is noteworthy to mention that passing of wastewater through the two layers of the spacer requires more time which leads to provide sufficient time for contact with the nanoparticles and consequently the photocatalytic process [30], [31], [32].
The main purpose of this study is to investigate the photocatalytic decolorization and mineralization of RBB using ZnO and TiO2 nanoparticles loaded on spacer fabric. The effects of the operational parameters on efficiency of the decolorization were evaluated to determine optimum condition. Moreover, the kinetics of the photocatalytic decolorization were investigated.
Section snippets
Materials
RBB (C26H21N5Na4S6, MW = 991.82 g/mol) was obtained from Alvan Sabet Co., Iran. The chemical structure of RBB is shown in Fig. 1. Nano powder of TiO2 (Degussa P-25) (with an average size of 21 nm and a combination of 80% anatase/20% rutile) and nano powder of ZnO (with an average size of <50 nm, zincite) were provided from Evonik, Germany and Sigma-Aldrich, USA, respectively. Spacer fabric (a surface string of 150 den, a beneath string of 150 den, a monofilament connector string of 30 den, a weight of
SEM images
Morphology of the samples was observed by scanning electron microscopy (SEM, LEO 1455VP, Cambridge, UK). Fig. 4(a and d) illustrates the SEM images of the untreated spacer fabric (a), the treated spacer with ZnO, CA and SHP (b), the treated spacer with TiO2, CA and SHP (c) and the treated spacer fabric with ZnO:TiO2, CA and SHP (d). The porous structure of the spacer (Fig. 4a) led to an increase in the capacity of the dye adsorption from wastewater. Also, Fig. 4 confirms that the surface
Conclusion
The decolorization of an azo reactive dye (Remazol Black B) in an aqueous solution by nano-photocatalytic systems (UV/H2O2/ZnO, UV/H2O2/TiO2 and UV/H2O2/ZnO:TiO2) was investigated. Effective parameters including initial pH value, initial H2O2 concentration, initial dye concentration, the loaded nanoparticle ratio and the presence of sodium salts (NaCl, Na2SO4 and NaHCO3) were evaluated. SEM images and EDS spectra confirmed the successful loading of the nanoparticles on the spacer fabrics. The
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