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Open AccessDOI: 10.12030/j.cjee.202506064Original Research

Electrocatalytic Oxidation Performance and Mechanism of Porous Active Metal Oxide Coated Anode for Congo Red Degradation

School of Life and Environmental Sciences, Guilin University of Electronic Technology, Guilin 541004, China

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Published In
Chinese Journal of Environmental Engineering
Published:January 15, 2026Edition:Vol. 20, Issue 5 • pp. 100-112Citation:HUANG Zijiao et al. (2026), Chinese Journal of Environmental Engineering
Impact FactorPeer-Reviewed Core
Source Journal环境工程学报

Key Takeaways & Executive Findings

  • • • Achieved 91% decolorization of Congo red within 20 min and 82% mineralization within 60 min under optimal conditions (5 mA·cm−2, 480 L·(m2·h)−1, 0.15 mmol·L−1 CR, 75 mmol·L−1 NaCl), demonstrating high efficiency for high-salinity wastewater treatment. • • Flow-through mode enhanced mass transfer with a rate constant of 2.23×10−4 m·s−1, three times higher than conventional mode, and reduced diffusion layer thickness to 2.68 μm, significantly improving pollutant-anode contact. • • Active chlorine and H2O2 production increased by 32.8% and 66.7% respectively, reaching 0.61 mmol·L−1 and 0.24 mmol·L−1, enabling efficient generation of singlet oxygen (1O2) as the dominant reactive species. • • The system achieved >90% decolorization for five typical dyes with an energy consumption of only 0.16 kWh·m−3, indicating cost-effectiveness and broad applicability for industrial textile effluents.

Abstract

To address the challenges of high salinity, recalcitrance, limited mass transfer, and coating detachment in traditional anodes for textile wastewater treatment, a porous RuO2@r-TiO2 nanotube array (NTA) anode was fabricated via anodic oxidation, electrochemical reduction, and thermal decomposition. A flow-through electrochemical oxidation system was constructed using this anode and a graphite felt cathode. The material's morphology and physicochemical properties were characterized by SEM, XRD, and XPS. Congo red (CR) was used as a model pollutant to evaluate degradation performance under various conditions. Optimal conditions were identified as current density 5 mA·cm−2, permeate flux 480 L·(m2·h)−1, initial CR concentration 0.15 mmol·L−1, and NaCl concentration 75 mmol·L−1. Under these conditions, the system achieved 91% decolorization within 20 min and 82% mineralization within 60 min. Mass transfer tests showed a rate constant of 2.23×10−4 m·s−1 in flow-through mode, three times higher than conventional mode, with active chlorine and H2O2 production increased by 32.8% and 66.7%, respectively. Radical quenching experiments indicated that singlet oxygen (1O2) was the primary reactive species. The degradation mechanism was proposed based on quenching and UV spectral analysis. The system achieved >90% decolorization for five typical dye pollutants with an energy consumption of only 0.16 kWh·m−3. Cyclic voltammetry confirmed long-term stability. These findings provide theoretical support for applying electrochemical advanced oxidation to high-salinity textile wastewater.

1. Introduction

Textile wastewater, characterized by high salinity, intense color, and poor biodegradability, poses a significant environmental challenge. Conventional treatment methods, including biological processes, often fail to meet discharge standards due to the recalcitrance of synthetic dyes. Advanced oxidation processes (AOPs) such as Fenton and ozonation are effective but suffer from high chemical consumption and secondary pollution. Electrochemical advanced oxidation processes (EAOPs) offer a promising alternative due to their mild conditions, no external chemical addition, and flexible operation. However, the performance of EAOPs is critically dependent on the anode material. Traditional plate anodes, such as DSA electrodes, exhibit limited mass transfer due to thick boundary layers (>100 μm), and their catalytic coatings often delaminate from the titanium substrate, leading to electrode deactivation and poor long-term stability.

To overcome these bottlenecks, this study introduces a porous RuO2@r-TiO2 nanotube array anode fabricated on a porous titanium foam substrate. The in-situ growth of TiO2 nanotube arrays enhances coating adhesion and provides a high surface area. Operating in flow-through mode, the porous structure significantly reduces the diffusion layer thickness, thereby improving mass transfer and the utilization of electrogenerated oxidants. This design directly addresses the limitations of conventional EAOPs, offering a more efficient and stable solution for the treatment of high-salinity dye wastewater.

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Cite This Research Paper
HUANG Zijiao, WEI Jiaqi, KONG Xinyi, CUI Jiayi, ZHANG Yuanyuan, WEI Qiaoyan, ZHENG Junjian, JU (2026). Electrocatalytic Oxidation Performance and Mechanism of Porous Active Metal Oxide Coated Anode for Congo Red Degradation. Chinese Journal of Environmental Engineering. https://doi.org/10.12030/j.cjee.202506064
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Frequently Asked Questions

What is the long-term stability of the RuO2@r-TiO2 NTAs anode under continuous operation?

Cyclic voltammetry tests confirmed the electrode's long-term stability, indicating that the RuO2 coating remains adhered to the TiO2 nanotube array substrate, preventing delamination and maintaining catalytic activity over extended periods.

How does the flow-through mode enhance mass transfer compared to conventional plate electrodes?

Flow-through mode reduces the diffusion layer thickness to 2.68 μm, significantly lower than the >100 μm boundary layer in conventional mode. This results in a mass transfer rate constant of 2.23×10−4 m·s−1, three times higher, thereby increasing the contact efficiency between pollutants and reactive species.

What is the energy consumption and scalability potential of this system for industrial application?

The system achieves an energy consumption of only 0.16 kWh·m−3, which is highly competitive. The use of porous titanium foam and scalable fabrication steps suggests potential for scale-up, though further pilot-scale studies are needed to assess long-term operational costs and electrode replacement frequency.

What is the dominant degradation mechanism for Congo red in this system?

Radical quenching experiments revealed that singlet oxygen (1O2) is the primary reactive species, generated from the reaction of electrogenerated H2O2 with active chlorine. The contribution of free radicals (·OH, Cl·, O2·−) is minor, accounting for only 19.8% of degradation.

How does the system perform with other dye pollutants besides Congo red?

The system achieved >90% decolorization for five typical dyes, including methyl orange, methylene blue, Coomassie brilliant blue, and malachite green, demonstrating broad-spectrum applicability for various dye structures and functional groups.

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