Electrocatalytic activation of peroxomonosulfate (PMS) under aerobic condition for the remediation of oil sands process water: Insight into one-pot synergistic coupling of PMS electro-activation and heterogeneous electro-Fenton processes

化学 矿化(土壤科学) 催化作用 降级(电信) 过氧二硫酸盐 高级氧化法 硫酸盐 采出水 过硫酸盐 猝灭(荧光) 流出物 环境修复 羟基自由基 核化学 氧化还原 激进的 环境化学 无机化学 有机化学 废物管理 污染 氮气 荧光 生物 工程类 电信 量子力学 物理 计算机科学 生态学
作者
Soliu Oladejo Ganiyu,Nora A.S. Hussain,James L. Stafford,Mohamed Gamal El‐Din
出处
期刊:Chemical Engineering Journal [Elsevier BV]
卷期号:480: 147737-147737 被引量:60
标识
DOI:10.1016/j.cej.2023.147737
摘要

Alkaline industrial effluents possess a different challenge during treatment by advanced oxidation processes due to the reduction in redox potential of hydroxyl radical (•OH) in basic media. Herein, electrocatalytic peroxomonosulfate activation (EC-PMS), which synergistically couples an early-stage PMS electro-activation (E-PMS) with subsequent heterogeneous electro-Fenton oxidation (HEF) catalyzed by Fe-modified biochar (BC-Fe) was investigated for enhanced degradation and mineralization of organics in oil sands process water (OSPW). The EC-PMS was first studied for the degradation of surrogate naphthenic acids (NAs) (5-phenylvalveric acid, (PVA)) as a synthetic process water and complete degradation of 50 mg L−1 PVA solution was achieved within very short treatment time (0.5 h) with excellent mineralization (>70 % TOC removal) in 6 h. The efficiency of EC-PMS for PVA degradation was affected by the applied current density, PMS, and catalyst dosage. The organic degradation, electroparamagnetic resonance spectrometry, quenching and chemical probe experiments showed that sulfate radical (SO4•−) generated by E-PMS was the dominant radical oxidant for the degradation of PVA, contributing over 93 %, whereas •OH produced from BC-Fe decomposition of electrogenerated H2O2 in HEF was responsible for the mineralization of the organic solution at the later stage of the coupled process. The EC-PMS showed excellent reusability and was effective for the treatment of real OSPW, achieving complete degradation of real NAs in OSPW and relatively good mineralization of the water. Analysis of the EC-PMS treated OSPW did not simulate any response during the bioactivity assay test using a macrophage cell line, indicating the complete detoxification of the water.

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