Transformation products and degradation pathway of textile industry wastewater pollutants in Electro-Fenton process
Introduction
Water contamination is a huge issue that the world is confronting today. It is expanding with each passing year, making grave and hopeless harm to the earth and environment. Textile industries are considered to be a major containment to the fresh water because of high toxicity and non-biodegradability of dye stuff and other chemicals. Direct discharge of textile wastewater is restricted to the environment by various environmental/pollution regulatory agencies. Unfortunately, due to biological resistance and chemical stability of dyes and other chemicals in textile wastewater, make it hardly treated by the conventional treatment methods (Georgiou et al., 2002; Meric et al., 2004; Izares et al., 2006; Chen and Liu., 2012; Bansal et al., 2013; Kaur et al., 2017), however, if treated huge volume of secondary pollutants are generated. Therefore, researchers have focused toward the treatment without generating secondary pollutants. Among all promising techniques, electro-oxidation is efficient to degrade toxic compounds in an aqueous phase, and demonstrated their great performance for the treatment of textile wastewater. However, generation of chloro-organic compounds during the treatment process is major drawback of electro-oxidation process. This drawback can be overcome by Electro-Fenton process (EF) (Brillas et al., 2009). The efficiency of the EF process predominantly depends on H2O2 production rate, O2 solubility, pH, anode material, Fenton catalyst and current intensity. Fenton catalyst concentration and type significantly affect the EF treatment efficiency. Various catalyst are reported in literature but Fe2+ or Fe3+ proved good catalytic characteristics even at lower concentrations (Sirés and Brillas, 2012). EF is based on the degradation of pollutants by the action of both Fenton's reaction Eq. (2) in the bulk and anodic oxidation at the anode surface Eq. (4). H2O2 is continuously generated in the solution during electrolysis in EF process due to two electron oxygen reduction at cathode (Brillas et al., 2009; Sirés et al., 2014) in an acidic medium Eq. (1), and ferrous ion added into the system analogously generates the OH radicals in the classical Fenton's reaction Eq. (2). At the same time, in this process, the ferrous ion is regenerated at the cathode Eq. (3). Ferric ions generated during EF process for monomeric and polymeric hydroxyl complexes.O2 + 2H+ + 2e− → H2O2Fe2+ + H2O2 → Fe3+ + OH− + OHFe3+ + e− → Fe2+M(H2O) → M(OH) + H+ + e−
Dimensionally stable anodes (DSAs) are stable during electrolysis, have high oxygen overvoltage and does not produce secondary pollutants (Brillas and Casado, 2002; Nasr et al., 2005). There are number of DSAs i.e titanium coated RuO2, IrO2, SnO2, PbO2; boron doped diamond electrodes; Pt/Ti etc. used by various researchers for electrochemical treatment processes (Wang et al., 2005; Zhou and He, 2007; Martinez-Huitle and Brillas., 2009; Salazar et al., 2012; Oturan et al., 2012; Pajootan et al., 2014; Mukimin et al., 2015; Mukimin et al., 2017). Fenton's reaction is applied in acidic pH of 2.8–3.0 (Sun and Pignatello, 1993) to efficiently produce OH. Ti/RuO2 electrodes are highly stable in acidic medium and it is an active DSAs electrode, provide large surface area for the adsorption of pollutants (Santos et al., 2010). Ti/RuO2 anode also favours the chlorine species-mediated oxidation in bulk. Due to this carcinogenic/toxic chlorinated organic compounds may be generated during the EF process. OH radical generation is prominent in EF process, which can mineralized chlorinated organic compounds by •OH mediated oxidation. Various investigations prove that EF is well able to reduce the strong nature, carcinogenic and toxic behaviour of textile wastewater (Santos et al., 2010; Salazar et al., 2012; Nidheesh and Gandhimathi, 2014; Lin et al., 2014; Pajootan et al., 2014; Ghanbari and Moradi, 2015; Asghar et al., 2015; Garcia-Segura and Brillas, 2016). In literature, no study has been reported on the textile industry wastewater treatment by continuous EF method. Researchers just examined about the treatment of simulated/model textile wastewater. Textile industry wastewater has number of components, which can advance or thwart the treatment process. Subsequently, execution examination and appropriateness of EF process require more investigation on textile industry wastewater.
In the present study, treatment of textile industry wastewater was performed by EF method in continuous mode using Ti/RuO2 electrodes. The EF process was optimized for various process parameters i.e. elapsed time (t), retention time (RT), current (i) and concentration of ferrous sulphate (CFe) (Fenton catalyst) for % chemical oxidation demand (COD) removal (X1), % color removal (X2) and energy consumed (X3). Spectrophotometric and GC-MS analysis at optimum conditions was performed to identify the degraded/transformation compounds for degradation mechanism during EF process as well as disposability of treated wastewater. Further, bioassay test was performed for toxicity analysis of treated textile wastewater in view of disposal quality. The persuasive mechanism of the treatment process was also purposed by GC-MS analysis. Moreover, degradation kinetics in terms of COD removal and color removal were investigated. Operating cost analysis of the continuous mode for per Kg of COD removal was also performed to determine the economic feasibility.
Section snippets
Wastewater and experimental setup
Textile industry wastewater was collected from Mink Blanket industry (Ludhiana, Punjab). Textile effluent contains high strength of dyes that were used in mink blanket industry. The characterization of textile wastewater for various water quality parameters is given in Table SM-1. The Cl¯ content of the textile wastewater was also analyzed and found to be 1682.50 mgL−1 with standard Volhard method. Cubical shape EF continuous reactor was fabricated of plexi glass sheet. The working volume of
Regression model fitting and ANOVA
Experiments suggested by CCD (Table 1) were performed to determine the response X1, X2 and X3 of continues EF process for textile industry wastewater. The best fitted RSM model was quadratic model. The quality of quadratic model was evaluated by exploiting sequential F-test, model summary and subsequent ANOVA. The adequate precision for the responses X1, X2 and X3 was 23.936, 17.712, 16.273 respectively, which indicate an adequate signal that the model can be used to navigate the design space.
Conclusions
The optimization of operational parameters in continuous mode for the textile industry wastewater was done successfully. Spectrophotometric and GC-MS analysis clearly showed that •OH mediated oxidation was prominent in the degradation process of textile wastewater components. Due to high chloride content in textile wastewater, chlorinated organic compounds were expected in the treated wastewater, however, GC-MS analysis revealed absence of chlorinated organic compounds. Some other
Acknowledgement
Authors acknowledge to the University Grant Commission, India to provide MANF fellowship (MANF-2015-17-PUN-49188) to the first author of this article.
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