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    Cu2+/HCO3/H2O2高级氧化体系降解酸性红GR的机制与原理

    Mechanism and Principles of Acid Red GR Degradation in the Cu2+/HCO3/H2O2 Advanced Oxidation System

    • 摘要: 为了解决偶氮染料酸性红GR废水难降解问题,本研究采用Cu2+活化HCO3/H2O2(BAP)高级氧化体系对其降解处理,并探究了体系反应机理以及各影响因素对降解效能的作用。结果表明:酸性红GR初始浓度为25 mg·L−1、HCO3浓度为10 mmol·L−1、H2O2浓度为4 mmol·L−1、Cu2+浓度为15 μmol·L−1条件下,反应20 min时酸性红GR去除率可达92.7%以上。由于pH处于中碱性条件(6.54~10.85)下,碳酸氢盐更多以HCO3形态存在,更易转化成碳酸根自由基(CO3);反之,酸性条件(3.07~4.98)下,HCO3存在较少,反应速率明显抑制。常见无机阴离子(H2PO4、SO42−、Cl、NO3)干扰均产生不同程度抑制效果,其中H2PO4影响最大,NO3影响最小。自由基捕获实验验证体系中存在多种活性氧化物种,其中CO3与单线态氧(1O2)起到主导作用,而羟基自由基(•OH)与超氧自由基(O2)参与反应但贡献有限,电子顺磁共振(EPR)直接证实了•OH、CO31O2的存在。结合紫外可见光谱和质谱图分析,初步推断酸性红GR降解主要通过偶氮键断裂、苯环开环、萘环氧化等原因。经总有机碳(TOC)分析,30 min时酸性红GR矿化度可达到49%。该体系在中性至碱性条件下即可实现对酸性红GR的高效降解,具备较宽的适用pH范围和温和的反应条件,研究结论有利于降低运行成本并提升印染废水实际处理中的可行性。

       

      Abstract: To address the refractory degradation of wastewater containing the azo dye Acid Red GR, this study employed a Cu2+-activated HCO3/H2O2 (BAP) advanced oxidation system for its degradation treatment, and investigated the reaction mechanism of the system as well as the effects of various influencing factors on the degradation efficiency. The results showed that under the conditions of an initial concentration of Acid Red GR at 25 mg·L−1, a concentration of HCO3 at 10 mmol·L−1, a concentration of H2O2 at 4 mmol·L−1, and a concentration of Cu2+ at 15 μmol·L−1, the removal rate of Acid Red GR could reach over 92.7% after 20 minutes of reaction. Due to the pH being in the medium to alkaline range (6.54 ~ 10.85), bicarbonate existed predominantly in the form of HCO3, which facilitated the generation of carbonate radicals (CO3); conversely, under acidic conditions (3.07 ~ 4.98), the limited availability of HCO3 markedly suppressed the reaction rate. Common inorganic anions (H2PO4, SO42−, Cl, NO3) all had inhibitory effects to varying degrees, among which H2PO4 had the greatest impact and NO3 had the least. Radical quenching experiments confirmed the presence of multiple reactive oxygen species in the system, among which CO3and singlet oxygen (1O2) played dominant roles, while hydroxyl radicals (•OH) and superoxide radicals (O2) participated in the reaction but made limited contributions. Electron paramagnetic resonance (EPR) spectroscopy directly confirmed the presence of •OH, CO3, and 1O2.Combined with the analysis of ultraviolet-visible spectra and mass spectra, it was preliminarily inferred that the degradation of Acid Red GR mainly occured through the cleavage of the azo bond, the opening of the benzene ring, and the oxidation of the naphthalene ring. Through total organic carbon (TOC) analysis, the mineralization degree of Acid Red GR reached 49% within 30 minutes.This system achieves efficient degradation of Acid Red GR under neutral to alkaline conditions, with a wide applicable pH range and mild reaction conditions. These findings help reduce operating costs and enhancing the feasibility of practical treatment of dyeing and printing wastewater.

       

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