Electro-Fenton method for the removal of methyl red in an efficient electrochemical system
Introduction
Azo dyes are widespread environmental pollutants related with many important industries such as textile, printing, and cosmetic manufacturing. With the increasing production of these dyes, the discharge of dye effluents at high concentration and strong color has caused serious environmental pollution because many of these dyes are toxic and recalcitrant to biodegradation [1], [2]. Due to the chemically and light stable characteristics of azo group, it is not easy to treat such wastewater by biological oxidation [3], [4]. Various traditional physical and chemical processes such as adsorption have been attempted for the treatment of these kinds of wastewater. However, these methods are usually non-destructive, inefficient or expensive. To reduce the dangerous accumulation of these dyes in the environment, substantial research efforts are underway with the objective of exploring sound technologies for such hard-to-treat wastewater.
Recently, a more efficient and non-selective process, advanced oxidation processes (AOPs), which generates powerful oxidant of hydroxyl radical has been extensively investigated [5], [6], [7], [8]. Among these AOPs, Fenton oxidation is particularly attractive because of its simplicity without requirement for special equipment and high efficiency in organic pollutants removal [9]. To avoid the disadvantages of traditional Fenton oxidation such as the potential risk in transportation of H2O2 and the loss of reactive activity, a modified process called electro-Fenton has been developed which combined with ferrous ion addition and the electro-generated H2O2 in situ. Hydrogen peroxide can be produced by a two-electron reduction of oxygen at appropriate cathodic potential on certain electrodes such as reticulated vitreous carbon, graphite and gas diffusion electrode [10], [11], [12].O2 + 2H+ + 2e− → H2O2
Thus, the strong oxidant of hydroxyl radical can be generated in the solution with the addition of Fe2+ as catalyst, and this active species can attack and initiate the oxidation of pollutant (RH) as shown below (Eqs. (2), (3), (4)),Fe2+ + H2O2 + H+ → Fe3+ + OH + H2OFe3+ + H2O2 → Fe2+ + OOH + H+OH + RH → R + H2O
The electro-Fenton has the advantage of allowing a better control of hydroxyl radical production. Though there are many reports on electro-Fenton process application for the degradation of organic pollutants such as benzene ring compounds [6], [13], [14] or pesticides [15], [16], [17], few works have paid attention to the application of this process for azo dye wastewater treatment. Kusvuran et al. compared different treatment methods for the decolorization of reactive black 5 azo dye including electro-Fenton process in an electrochemical cell separated by expensive Nafion 117 membrane [7]. It was found that the dye degradation was only 50% when the initial dye concentration was higher than 40 mg/L. Wang et al. used an activated carbon fiber felt cathode for the electro-Fenton degradation of acid red 14, however the hydrogen peroxide production on this cathode was not higher than 0.6 mM in 180 min, which led to a long time (600 min) to degrade the dye [18]. Generally, the degree of dye oxidation would depend on the concentration of hydrogen peroxide in Fenton reaction. Therefore, to promote azo dye degradation, a highly efficient cathode system for effective production of hydrogen peroxide seems to be very important.
In our previous work, a home-made cathode system was developed, which showed high current efficiencies and hydrogen peroxide productions under wider pH ranges of 3–11 [19]. Thus in the present work, such a system was applied to the electro-Fenton oxidation of dye wastewater using methyl red as a model azo dye. The aim of the present work was to investigate the decolorization feasibility of this cathode system and disclose the influence of various parameters on dye removal. The effects of pH, cathodic potential, dosage of ferrous ion, electrolyte concentration and initial concentration of methyl red were systematically examined. In addition, the UV–vis spectra of methyl red during the treatment were also investigated.
Section snippets
Reagents and chemicals
Methyl red (Fisher Scientific Worldwide Company, Hong Kong) was used without further purification, and its structure is shown in Fig. 1. Other chemicals including anhydrous Na2SO4, H2SO4, FeSO4·7H2O and ethanol were analytic grade. The polytetrafluoroethylene (PTFE) (60 wt%) used was bought from 3F New Materials Co. Ltd., Shanghai, China.
Cathode fabrication
An appropriate amount of graphite powder and PTFE dispersion was added and mixed in an ultrasonic bath for 10 min at room temperature. Then ethanol was
Hydrogen peroxide production performance
One major concern of the electro-Fenton process is to improve the production and current efficiency for the formation of hydrogen peroxide on site. Numerous efforts have been made, utilizing different electrochemical systems and cathodes such as reticulated vitreous carbon, graphite or carbon-PTFE. Table 1 compares the performance of the present work with some literatures. Apparently, different electrodes varied greatly both on hydrogen peroxide generation rate (HPGR) and current efficiency.
Conclusions
Methyl red could be degraded quickly and efficiently by electro-Fenton process using the efficient electrochemical system. The solution pH not only affected the production of hydrogen peroxide, but also controlled the existence species of ferrous catalyst, which showed a better performance for methyl red degradation at pH 3. Hydrogen peroxide concentration showed the best at the cathodic potential of −0.55 V versus SCE, which resulted in the optimal removal of methyl red. The presence of Fe2+
Acknowledgments
We would like to acknowledge financial support of this work provided by the National Science Foundation of China (Grant No.20306027 and 20676121), the Science Foundation of Zhejiang Province (Grant No. Y504129) and Pao's Scholarship.
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