氯离子影响过硫酸盐降解苯酚的效果及机理
Impact mechanism of chloride ion on the degradation of phenol by persulfate
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摘要: 为研究氯离子 (Cl−) 影响过硫酸盐 (PS) 高级氧化技术修复苯酚污染地下水的效果及机理,采用热活化PS氧化体系考察温度、PS浓度、初始pH值及Cl−浓度对苯酚降解效果的影响,结合平行因子分析查明苯酚降解过程中体系的光谱特征,借助气相色谱-质谱联用仪识别氯代有毒副产物的数量及种类,并揭示其降解机理。结果表明:①反应温度的升高和PS浓度的增加均可促进苯酚的降解,且降解过程符合伪一级动力学模型;②Cl⁻的存在会加速热活化PS对苯酚的降解,其降解效率随Cl⁻浓度的增加而增强,当Cl−浓度为10、25和50 mmol/L时,反应5 h后苯酚降解率为100%。③苯酚降解过程中反应体系的荧光特征分可为4组分(C1、C2、C3和C4)模型,Cl−存在时,C1和C2组分的荧光强度下降幅度更大,C3和C4组分主要为苯酚降解产物的光谱特征,其中C3组分的荧光强度随反应时间延长呈先增强后降低趋势。④根据质谱测试结果推断Cl−存在时苯酚降解的可能机理,主要包括羟基化/氧化和氯化作用,其中生成的氯代有毒副产物包括2-氯苯酚、4-氯苯酚、2,4-二氯苯酚、氯氢醌、3,5-二氯儿茶酚、2,3-二氯-2-甲基丁烷和2-氯-4-甲基-2-戊醇。研究显示,Cl−会提升热活化PS对苯酚污染地下水的修复效率,但也会因氯化作用生成氯代有毒副产物,该结果可为苯酚污染地下水PS氧化技术的环境安全评价提供支撑。Abstract: To study the impact mechanism of chloride ion (Cl−) on the remediation of phenol-contaminated groundwater by persulfate (PS) advanced oxidation technology. The effects of temperature, PS concentration, initial pH value, and Cl− concentration on the degradation of phenol were investigated by thermal activated PS advanced oxidation technology. The spectral characteristics of the reaction solution during phenol degradation were identified by parallel factor analysis. Moreover, the quantities and species of chlorinated toxic by-products were identified by gas chromatography coupled to mass spectrometry, and the degradation mechanism was revealed. The results showed that: (1) Degradation of phenol was promoted by increasing the reaction temperature and PS concentration, and the degradation process was in accordance with the pseudo-first-order kinetics model. (2) The presence of Cl⁻ accelerated the degradation of phenol by thermal activated PS, and the degradation efficiency increased with the increase of Cl⁻ concentration. When Cl− concentration was retained at 10, 25, and 50 mmol/L, the degradation rate of phenol was reached 100% after the reaction of 5 h. (3) The fluorescence characteristics of the reaction solution can be divided into a four-component model (C1, C2, C3 and C4) during the degradation of phenol. Fluorescence intensity of C1 and C2 components decreased more significantly in the presence of Cl−. C3 and C4 components are assigned to the degradation products of phenol, and the fluorescence intensity of C3 increased first and then decreased during the reaction. (4) Seven chlorinated toxic by-products (2-chlorophenol, 4-chlorophenol, 2,4-dichlorophenol, chlorohydroquinone, 3,5-dichlorocatechol, 2,3-dichloro-2-methylbutane, and 2-chloro-4-methyl-2-pentanol) were detected, and the degradation mechanism was proposed using the mass spectrometry, including hydroxylation/oxidation and chlorination process. The study showed that Cl− can promote the remediation efficiency of thermal activated PS for phenol-contaminated groundwater, but also induce the generation of chlorinated toxic by-products due to the chlorination process, which will provide support for environmental safety evaluation of PS advanced oxidation technology for phenol-contaminated groundwater.
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Key words:
- chloride ion /
- persulfate /
- phenol /
- parallel factor analysis /
- chlorinated toxic by-products /
- degradation mechanism
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