A Review on Electrochemical Advanced Oxidation Treatment of Dairy Wastewater

Ashish Kumar Das, Lide Chen
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Abstract

Dairy wastewater (DW) contains a high concentration of organic and inorganic pollutants. In recent years, extensive research has been conducted to develop more efficient techniques for the treatment of DW. Electrochemical advanced oxidation processes (EAOPs) have gained significant attention among the various treatment approaches. EAOPs rely on electrochemical generation of hydroxyl radicals (•OH) which are considered highly potent oxidizing compounds for the degradation of pollutants in DW. In this paper, we provide an overview of the treatment of DW using various EAOPs, including anodic oxidation (AO), electro-Fenton (EF), photo electro-Fenton (PEF), and solar photo electro-Fenton (SPEF) processes, both individually and in combination with other techniques. Additionally, we discuss the reactor design and operating parameters employed in EAOPs. The variation in degradation efficiency is due to different oxidizing agents produced in specific approaches and their pollutant degradation abilities. In AO process, •OH radicals generated on electrode surfaces are influenced by electrode material and current density, while EF procedures use Fe2+ to create oxidizing agents both on electrodes and in the DW solution, with degradation mechanisms being affected by Fe2+, pH, and current density; additionally, PEF and SPEF approaches enhance oxidizing component production and pollutant degradation using ultraviolet (UV) light. Integration of EAOPs with other biological processes can enhance the pollutant removal efficiency of the treatment system. There is a scope of further research to exhibit the effectiveness of EAOPs for DW treatment in large scale implementation.
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电化学高级氧化法处理乳制品废水综述
乳制品废水(DW)含有高浓度的有机和无机污染物。近年来,人们为开发更高效的 DW 处理技术进行了广泛的研究。在各种处理方法中,电化学高级氧化工艺(EAOPs)备受关注。EAOPs 依靠电化学生成羟基自由基 (-OH),而羟基自由基被认为是降解污水中污染物的高效氧化化合物。本文概述了利用各种 EAOPs(包括阳极氧化 (AO)、电-芬顿 (EF)、光-电-芬顿 (PEF) 和太阳能光-电-芬顿 (SPEF) 工艺)单独或与其他技术结合处理 DW 的情况。此外,我们还讨论了 EAOPs 采用的反应器设计和运行参数。降解效率的变化是由特定方法中产生的不同氧化剂及其污染物降解能力造成的。在 AO 过程中,电极表面产生的 -OH 自由基受电极材料和电流密度的影响;而 EF 程序则利用 Fe2+ 在电极上和 DW 溶液中产生氧化剂,降解机制受 Fe2+、pH 值和电流密度的影响;此外,PEF 和 SPEF 方法利用紫外线 (UV) 增强氧化成分的产生和污染物的降解。将 EAOPs 与其他生物过程相结合,可以提高处理系统的污染物去除效率。还需要进一步研究,以展示 EAOPs 大规模应用于污水处理的有效性。
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