Recent Advances in Energy, Environment and Economic Development Chemical modification of graphite felts for efficient H2O2 production: Influence of operational parameters LEI ZHOU, MINGHUA ZHOU* College of Environmental Science and Engineering Nankai University Weijin Road 94 CHINA [email protected] Abstract: - Electro-Fenton process (EF) is a promising method for degradation of refractory pollutants in aquatic environment. The suitable cathode which produces hydrogen peroxide by oxygen reduction still plays a key role in the efficiency improvement of the EF. In this study, hydrazine hydrate-ethanol system was used to modify graphite felts, and the influence of the concentration of hydrazine hydrate on the production and efficiency of hydrogen peroxide was discussed based on the SEM and CV characterizations. The results showed that at a constant potential of -0.65 V (vs. SCE) the modified electrodes had much higher catalytic activity than the unmodified one. Operational parameters such as cathodic potential, pH and aeration amount were also investigated. The maximum yields of H2O2 obtained at -0.75 V (vs. SCE) in 0.05M Na2SO4 aqueous solution with oxygen mass flow rate at 0.4 L/min was 198.5 mg/L after 90 min. Thus, this chemical modification was a promising approach to promote the H2O2 electro-generation of carbon cathodes. Key-Words: - Graphite felts; Hydrazine hydrate; Chemical modification; H2O2; Oxygen reduction reaction; Electro-Fenton carbonaceous electrodes by changing their surface functional groups. In the present work, hydrazine hydrate-ethanol system was used to modify graphite felts, and the influence of the concentration of hydrazine hydrate on the production and efficiency of hydrogen peroxide was discussed based on the SEM and CV characterizations. Operational parameters such as cathodic potential, pH and aeration amount were also investigated, and the experimental results were presented. 1 Introduction As an environmentally friendly electrochemical technology, Electro-Fenton process (EF) is a promising method for degradation of refractory pollutants in aquatic environment [1,2]. The EF process is based on the continuous in-situ electrogeneration of H2O2, which can eliminate acquisition, shipment and storage, along with the addition of iron catalysts to produce oxidant ·OH. Therefore, the major concern with the EF system relates to the improvement of H2O2 production. Carbonaceous materials are widely used as cathodes due the advantages such as nontoxic, good stability, conductivity and chemical resistance, high overpotential of hydrogen evolution, and low catalytic activity of H2O2 decomposition [2]. Recently, several carbonaceous electrodes were reported such as graphite [3], reticulated vitreous carbon [4], activate carbon fiber [5,6], carbon sponge [7], carbon/ graphite felt [8-11], carbonaceous PTFE combined electrode [12-14], and metal-modified carbonaceous electrode [15,16]. The carbon/ graphite felt electrode has a high specific surface area favoring the fast generation of H2O2, mechanical integrity and easily acquisition, which make it a promising cathode material. Chemical modification is an efficient way to improve the electrochemical activity of the ISBN: 978-1-61804-139-5 2 Experimental 2.1 Preparation of cathode materials All chemicals used in this study were analytical grade and used without further purification. The commercial graphite felts (Shanghai Qijie Carbon material Co., LTD) with a specific surface area of about 0.6 m2·g-1 were degreased in an ultrasonic bath with acetone and deionized water in sequence, dried at 80 °C for 16 h, and then annealed at 150 °C for 2 h. These pretreated materials were marked as CF. A series of modified electrodes were prepared as follow. The pretreated graphite felts were immersed in 100 mL mixture of ethanol and hydrazine hydrate, and after refluxing at 60 °C for 6h, the samples were annealed at 150 °C for 2 h. 154 Recent Advances in Energy, Environment and Economic Development Since the volume concentration of the hydrazine hydrate in the mixture were 5%, 10%, 15% and 20%, the modified electrodes were marked as CFHA-5%, CF-HA-10%, CF-HA-15% and CF-HA20%, respectively. 3 Results and discussions 3.1 Morphologies and properties of graphite felts a 2.2 Characterization For a morphology characterization of graphite felt electrodes, a field-emission scanning electron microscopy (FE-SEM, LEO1530VP) was used. The contact angle of water on the electrode surface is examined by a contact angle meter (OCA15, Dataphysics). Electrochemical measurements were carried out with CHI660D workstation (CH Instruments, Chenhua, Shanghai, China) in a threeelectrode cell system at ambient temperature. b 2.3 Electro-generation of H2O2 The H2O2 electro-generation experiments were performed in a 0.13 L undivided three-electrode cell using CHI660D electrochemical workstation as power supply. The prepared cathode (5 cm×2 cm×0.5 cm) was used as working electrode, a platinum wire as counter electrode and a saturated calomel electrode (SCE) as reference electrode. The distance between the working electrode and counter electrode was 3.5 cm. Prior to the electrolysis, oxygen (96% purity) was bubbled near the cathode through the 0.05 M Na2SO4 aqueous solutions for 10 min, and then oxygen was reduced at a desired potential (vs. SCE) on the working electrode for 90min, with a constant magnetic stirring of 300 rpm. The concentration of H2O2 during electro-generation process (C) was monitored by UV-vis spectrophotometer (UV759, Shanghai instrument analysis instrument Co., LTD) using the potassium titanium (IV) oxalate method [17]. The current efficiency (CE) for H2O2 production was defined as follow [18]: nFCH O V CE = t 2 2 ×100 % Fig. 1 SEM images of (a) CF and (b) CF-10% Fig. 1a and 1b show the SEM images of CF and CF-10%. It was observed that the graphite felts were composed of an entangled network of carbon microfilaments with diameter around 20 µm, and this structure form could contribute to the large gasliquid contact interfaces. After chemical modification, the longitudinal etching trace on the fiber increased, and many carbon particles and clusters with an average diameter of about 500 nm were appeared on the surface. The changes in the microstructures of modified samples could effectively increase the specific surface areas and the number of active sites, which were considered to be conducive to the catalytic process. ∫ Idt 0 Where n is the number of electrons transferred for oxygen reduction to H2O2, F is the Faraday constant (96 486 C/mol), CH2O2 is the concentration of H2O2 (mg/L), V is the bulk volume (L), I is the current (A), and t is the time (s). ISBN: 978-1-61804-139-5 3.2 Effect of the concentration of hydrazine hydrate 155 Recent Advances in Energy, Environment and Economic Development 160 140 80 120 60 100 40 CE (%) Concentration (mg/L) To further investigate the effects of chemical modification on electrocatalytic activity of cathodes toward ORR, cyclic voltammetry was carried out at graphite felts before and after modification as Fig. 3 shown. Standard voltammograms with total irreversibility were obtained for all samples, and the modified cathodes exhibited stronger current responses and more negative hydrogen evolution potentials than unmodified one, suggesting that modified samples had higher activities for oxygen reduction, which promoted the H2O2 production. Moreover, with the increasing concentration of hydrazine hydrate the current response for cathodes became stronger. It was also seen that the modification not only encouraged the two-electron transfer process towards ORR (i.e. H2O2 electrogeneration, Eq. 1), but also enhance the other ORR processes, which might be competition for the H2O2 generation (Eqs. 2, 3), resulting in a drop of current efficiencies for modified electrodes. 100 80 20 60 40 0 0 5 10 15 20 Concetration of hydrazine hydrate (%) Fig. 2 The effects of the precursors on H2O2 production. Conditions: E= -0.65 V vs. SCE, 0.05M Na2SO4, pH=7, O2 flow rate at 0.4L/min. The concentrations of hydrogen dioxide and current efficiencies for cathodes before and after modification were shown in Fig. 2. After 90min, the concentrations of H2O2 for CF, CF-HA-5%, CFHA-10%, CF-HA-15% and CF-HA-20% were 52.7, 122.4, 144.7, 139.0 and 134.5 mg/L, respectively. The enhanced yields of H2O2 after modification indicated the positive effects of precursors on H2O2 electro-generation. In addition, the optimum concentration of the hydrazine hydrate was detected, and among the modified electrodes the CF-HA-10% showed the highest yield of H2O2. When the concentration of the hydrazine hydrate exceeded the optimum, a little decrease in the catalytic activity was observed under the constant potential of -0.65 V vs. SCE. The current efficiencies of CF, CF-HA5%, CF-HA-10%, CF-HA-15% and CF-HA-20% were 89.1%, 86.8%, 85.1%, 80.3% and 73.7%, respectively. It was seen that the current efficiencies declined with the increasing concentration of hydrazine hydrate used in chemical modification. O 2 + 2H + + 2e − → H 2 O 2 O 2 + 4H + + 4e − → 2H 2O H 2 O 2 + 2H + + 2e − → 2H 2O (1) (2) (3) With the increasing concentration of hydrazine hydrate in modification, the ORR tended to the higher number electron transfer for each oxygen molecule under the same potential. In addition, the enhanced current in the system promoted the parasitic reactions at anode (Equ. 4, 5), which resulted in a decreased H2O2 accumulation and lower current efficiency [19]. H 2 O 2 → HO 2 ⋅ + H + + e − (4) HO 2 ⋅ → O 2(g) + H + + e − (5) 3.3 Effect of cathodic potential 0 100 200 -1 80 Concentration (mg/L) 2 -2 CF CF-HA-5% CF-HA-10% CF-HA-15% CF-HA-20% -3 -4 -1.6 60 120 40 80 20 40 -1.4 -1.2 -1.0 -0.8 -0.6 -0.4 -0.2 0.0 0 -0.9 Potential (V) -0.8 -0.7 -0.6 -0.5 -0.4 0 -0.3 Potential (V) Fig. 3 Cyclic voltammograms of the cathodes obtained in the potential range from -1.4 to 0 V (vs. SCE), in 0.05M Na2SO4 solution, at the scan rate of 50mV·s-1 ISBN: 978-1-61804-139-5 CE (%) j (mA/cm ) 160 Fig. 4 The effects of the potentials (vs.SCE) on H2O2 production. Conditions: using CF-HA-10% as cathode, 0.05M Na2SO4, pH=7, O2 flow rate at 0.4L/min. 156 Recent Advances in Energy, Environment and Economic Development the higher level of hydrogen ion also promoted the decomposition of H2O2 (Eq. 2). As a result, the obtained results showed that pH did not dramatically influence the accumulation of H2O2, which was similar with the results of previous studies [7,20], but the current efficiencies declined due to the increasing side reactions in acid solution. The effects of the potential on H2O2 production at CF-HA-10% cathode were shown in Fig. 4. The accumulations of H2O2 at the potential ranging from -0.35 V to -0.85 V were 15.7, 46.4, 106.0, 144.7, 198.5 and 149.5 mg/L, respectively. It can be seen that the H2O2 electro-generation initially enhanced with the increasing cathodic potential (|E|), and then declined when exceeded the potential of -0.75 V, at which the maximum yield of H2O2 was obtained. The current efficiencies of H2O2 production at the potential ranging from -0.35 V to -0.85 V were 97.2%, 89.7%, 87.1%, 82.0%, 64.3% and 41.7%, respectively. As CV curves confirmed, the competing reactions were also enhanced after modification, which could become more and more remarkable with the cathodic potential increasing. Hence, the current efficiencies went downhill quickly, although the yields of H2O2 were improved. When the cathodic potential became more negative than -0.75 V, the side reactions corresponding to the H2O2 decomposition and higher number electron transfer became dominant, which resulted in a decreased yields and current efficiencies of H2O2. 3.5 Effect of oxygen mass flow rate 160 140 80 Concentration (mg/L) CE (%) 0 6 7 8 9 10 pH Fig. 5 The effects of the pH on H2O2 production. Conditions: using CF-HA-10% as cathode, E= -0.65 V vs. SCE, 0.05M Na2SO4, O2 flow rate at 0.4L/min. The effects of the pH on H2O2 production at CFHA-10% cathode were shown in Fig. 5. When pH=3~9, the concentrations of H2O2 were 158.9, 152.1, 144.7 and 138.0 mg/L, and the current efficiencies were 68.9%, 75.5%, 85.0% and 86.1%, respectively. There was a slight increase of the electro-generated H2O2 with the increasing pH. Since H2O2 was electro-generated at cathode surface by reduction of dissolved oxygen in acidic medium, as Equ. 1 shown, from this point of view, the lower pH was beneficial to the H2O2 production. However, ISBN: 978-1-61804-139-5 0.6 The effects of the aeration amount on H2O2 production at CF-HA-10% cathode were shown in Fig.6. The accumulation of H2O2 at O2 flow rate of 0, 0.2, 0.4 and 0.6 L/min were 16.8, 100.2, 144.7 and 129.2 mg/L, and the current efficiencies were 35%, 77.5%, 85.1% and 94.0%, respectively. The increasing aeration amount could enhance the concentration of dissolved O2 and promote the mass transfer rate of dissolved O2 in solution, which were conducive to the H2O2 electro-generation. However, when O2 flow rate reached to 0.6 L/min, the resistance of the medium increased with a mass of bubble in the constant potential system, and then the current declined, inducing a little drop in the yields of H2O2. The result indicated that too much aeration could impede the H2O2 production. 20 5 0.4 Fig. 6 The effects of the aeration amount on H2O2 production. Conditions: using CF-HA-10% as cathode, E= -0.65 V vs. SCE, 0.05M Na2SO4, pH=7. 110 4 0.2 Aeration Amount (L/min) 120 3 0 0.0 60 2 40 0 140 100 40 60 20 150 40 60 80 20 80 130 100 CE (%) Concentration (mg/L) 120 3.4 Effect of pH 160 100 4 Conclusion In this study, hydrazine hydrate-ethanol system was used to modify graphite felts. After modification, a larger specific surface area was observed by SEM, which was considered to be conducive to the catalytic process. The modified samples had much higher electro-catalytic activity of oxygen reduction than the bare one, and the concentration of H2O2 generated was doubled after modification. Besides, there was an optimum 157 Recent Advances in Energy, Environment and Economic Development application to degradation of synthetic dye basic blue 3 in aqueous medium, Journal of Electroanalytical Chemistry, Vol.616, No.1-2, 2008, pp. 71-78. [8] M. Panizza, M.A. Oturan, Degradation of Alizarin Red by electro-Fenton process using a graphite-felt cathode, Electrochimica Acta, Vol. 56, No.20, 2011, pp. 7084-7087. [9] S. Hammami, N. Oturan, N. Bellakhal, M. Dachraoui, M.A. Oturan, Oxidative degradation of direct orange 61 by electroFenton process using a carbon felt electrode: Application of the experimental design methodology, Journal of Electroanalytical Chemistry, Vol.610, No.1, 2007, pp. 75-84. [10] M.H. Zhou, Q.Q. Tan, Q. 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Wang, et al., Electrogeneration of hydrogen peroxide on a novel highly effective acetylene black-PTFE cathode with PTFE film, Electrochimica Acta, Vol.56, No.24, 2011, pp. 8651-8656. [15] M.H.M.T. Assumpção, A. Moraes, R.F.B. De Souza, et al., Low content cerium oxide nanoparticles on carbon for hydrogen peroxide electrosynthesis, Applied Catalysis A: General, Vol.411-412, 2012, pp.1-6. [16] J.L. Fu, X.W. Zhang, L.C. Lei. Fe-modified multi-walled carbon nanotube electrode for production of hydrogen peroxide, Acta Physico-Chimica Sinica, Vol.23, No.8, 2007, pp. 1157-1162. [17] R.M. Sellers. Spectrophotometric determination of hydrogen peroxide using concentration for the precursor. The maximum yields of H2O2 obtained at -0.75 V (vs. SCE) in 0.05M Na2SO4 aqueous solution with oxygen mass flow rate at 0.4 L/min was 198.5 mg/L after 90 min, and the results indicated a dramatically influence of the applied potentials on the H2O2 production. 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