First, the brush was fully characterized in terms of its electrical conductivity and surface area. Its interfacial charge-transfer resistance (Rct) – as determined by electrochemical impedance spectroscopy – equaled 1.40 Ω. Cyclic voltammetry was used to determine the electroactive surface area of the electrode, which was found equal to 416 cm2, by using the Randles-Sevcik equation (Eq. 1):
Ip = 2.69 × 105 × AD1/2n1/2γ1/2C (Eq. 1)
where Ip is the peak current (A), n is the number of electrons participating in the redox reaction (n = 1), A is the area of the electrode (cm2), D is the diffusion coefficient of the molecule in solution (7.60 × 10-6 cm2 s-1), C is the concentration of the probe molecule in the bulk solution (1 × 10-5 mol cm-3), and γ is the scan rate of the potential perturbation (0.01 V s-1).
The catalytic activity of the novel electrode was then assessed by its capacity to electrogenerate H2O2. Since H2O2 is an intermediate required to produce •OH in the electro-Fenton reaction (Eq. 2) and is easier to detect, due to its longer half-life, its production arguably constitutes a better indicator of the cathode efficiency than the generation of •OH (4, 5):
H2O2 + Fe2+ → Fe3+ + •OH + HO- (Eq. 2)
The influence of the current density (normalized to the cathode projected surface area) on H2O2 production through cathodic reduction of O2 was thus evaluated and the best results were obtained at 1.25 mA cm-2, yielding a specific maximum H2O2 concentration of 3.00 ± 0.12 mg-H2O2 L-1 cm-2. Upon addition of Fe2+ to trigger the electro-Fenton reaction following Eq. 2, a mineralization efficiency of 80% was attained within 3 hours using real wastewater from the microelectronics industry in a lab-scale batch setup (Fig. 1) and the energy requirement was as low as 0.14 kWh g-1of total organic carbon (TOC).
Following these promising results, a continuous-flow pre-pilot scale prototype was designed and a computational flow simulation allowed optimizing various parameters, from electrode spacing to flowrate and mass transfer rates towards the electrodes (Fig. 2). The performance of this pre-pilot prototype was evaluated in the same conditions as the lab-scale reactor, confirming and even improving the results obtained at lab-scale with over 90% TOC removal reached within 3 hours (Fig. 1). However, the energy consumption increased with the intensity of the treatment from 0.8 KWh g-1 of TOC in the first hour to 1.34 kWh/g-1of TOC, after 3 hours, showing that electro-Fenton would be better used as a pre-treatment technology, over a limited period of time. Overall, these results demonstrate the potential of electro-Fenton as a water treatment and reuse technology and constitute an important step towards full-scale applications. A detailed technical economic assessment of the technology for industrial water reuse will be presented at the conference.
References
1. E. Mousset, Z. T. Ko, M. Syafiq, Z. Wang and O. Lefebvre, Electrochim. Acta (in press).
2. E. Mousset, Z. Wang, J. Hammaker and O. Lefebvre, Electrochim. Acta, 214, 217 (2016).
3. E. Mousset, Z. Wang and O. Lefebvre, Water Sci. Technol., 74, 2068 (2016).
4. L. Zhou, M. Zhou, Z. Hu, Z. Bi and K. G. Serrano, Electrochim. Acta, 140, 376 (2014).
5. F. Yu, M. Zhou and X. Yu, Electrochim. Acta, 163, 182 (2015).