改性电极-电芬顿体系对磺胺甲噁唑的降解效能及其路径

Degradation efficiency and pathway of modified electrode and electric-Fenton system for sulfamethoxazole

  • 摘要: 近年来,抗生素污染已在全球范围引起广泛关注,为探索绿色节能的含抗生素废水处理工艺,采用γ-FeOOH和CeO2分别制备改性阴极,深入探究其在电芬顿系统(传统芬顿反应结合电化学高级氧化技术)及生物电芬顿系统(利用微生物产生的电能驱动电芬顿反应)中对常规污染物及磺胺甲噁唑的去除效果。结果表明:在微电环境下电芬顿系统中,γ-FeOOH改性电极展现出优异性能,900 mV条件下,其对COD、TOC和磺胺甲噁唑的去除率分别达到72.5%、63.0%和91.6%;300 mV条件下,其对COD和TOC的去除率高于对照组在900 mV时的去除率,表明改性电极在低电压下即可实现高效的污染物去除,显著优于单纯提高电压的传统方法,且能够有效节约电能。在生物电芬顿系统中,改性电极对COD和TOC的去除效果显著提升。其中,γ-FeOOH改性电极对COD和TOC的去除率均提升了15个百分点以上,对磺胺甲噁唑的去除率提高了40个百分点以上。通过对磺胺甲噁唑降解产物的分析,推测其降解的两条途径分别为以4-氨基苯磺酸为中间产物并逐步矿化为甲烷,以及通过硝化和脱硝反应后实现矿化。研究结果可为开发高效电极材料、生物微电利用及高效节能水处理工艺提供技术支持。

     

    Abstract: In recent years, antibiotic pollution has garnered widespread global attention. To explore green and energy-efficient treatment processes for antibiotic-contaminated wastewater, this study employed γ-FeOOH and CeO2 to fabricate modified cathodes and investigated their performance in electric-Fenton (the Fenton reaction combining with electrochemical advanced oxidation processes) and bio-electric-Fenton systems (utilize the electrical energy generated by microorganisms to drive the electro-Fenton reaction) for the removal of conventional pollutants and sulfamethoxazole. The results demonstrated that the γ-FeOOH-modified electrode exhibited superior performance under a micro-electrochemical environment. At 900 mV, the removal rates of COD, TOC, and sulfamethoxazole reached 72.5%, 63.0%, and 91.6%, respectively. Notably, at 300 mV, the removal rates of COD and TOC by the γ-FeOOH-modified electrode exceeded those of the control group at 900 mV, indicating that the modified electrode could achieve efficient pollutant removal at a lower voltage, outperforming the traditional method of simply increasing the voltage and effectively saving electrical energy. In the bio-electric-Fenton system, the removal efficiency of the modified electrode for COD and TOC was significantly enhanced. The removal rates of COD and TOC by the γ-FeOOH-modified electrode increased by over 15 percentage points, while the removal rate of sulfamethoxazole was enhanced by more than 40 percentage points. By analyzing the degradation products of sulfamethoxazole, two potential pathways for its degradation were suggested. One was gradual mineralization to methane via 4-aminobenzenesulfonic acid as an intermediate, and the other was mineralization through nitrification and denitrification reactions. The research results can provide technical support for the development of efficient electrode materials, the utilization of biomicroelectronics and energy-efficient water treatment processes.

     

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