Environmental Engineering and Science Program, Department of Chemical and Environmental Engineering, University of Cincinnati, Cincinnati, USA.
Department of Chemistry and Biochemistry, Florida International University, Miami, USA.
Water Res. 2020 Mar 15;171:115394. doi: 10.1016/j.watres.2019.115394. Epub 2019 Dec 13.
The bicarbonate and carbonate ions (HCO &CO) will consume hydroxyl radical (HO) to generate carbonate radical anion (CO) in hydroxyl radical based advanced oxidation processes (HO-AOPs) resulting in reduced oxidation efficiencies of the systems. However, despite the HO quenching effect of carbonate species, the contribution of CO to the degradation of bisphenol A (BPA) was observed in UV/sodium percarbonate (UV/SPC). In order to study the performance of UV/SPC for BPA degradation and the role of CO in this process, the degradation kinetics and mechanisms of BPA in UV/SPC and in UV/hydrogen peroxide (UV/HO) were compared at equivalent concentration of HO. In this study, the observed degradation rates of BPA by UV/SPC and by UV/HO in Milli-Q water were similar. Variation of the BPA degradation rates in the presence of radical quenchers, tert-butanol and phenol, suggested that both CO and HO contributed to the degradation of BPA in UV/SPC. Second order rate constant of CO towards BPA ( [Formula: see text] = 2.23 × 10 M s) and steady state concentrations of CO ( [Formula: see text] = 2.3 × 10 M) and HO ( [Formula: see text] = 1.82 × 10 M) in UV/SPC were determined with competition kinetics at 1 mM SPC and pH 8.5. The high [Formula: see text] observed in UV/SPC compensated for the smaller [Formula: see text] compared to [Formula: see text] and the consumption of HO making the degradation rate of BPA in UV/SPC comparable to that in UV/HO. Detailed studies on identification of transformation products (TPs) of BPA in UV/SPC revealed that phenol ring and isopropylidene bridge were the main reactive sites of BPA. Degradation pathways were proposed accordingly. The results of kinetic and mechanistic studies provide better fundamental understanding of the degradation of BPA in UV/SPC and HCO&CO impact on BPA degradation by HO-AOPs. This also demonstrates potential for CO based water purification technologies.
在羟基自由基基高级氧化工艺(HO-AOPs)中,碳酸氢根和碳酸根离子(HCO₃&CO₃)会消耗羟基自由基(HO)生成碳酸根自由基阴离子(CO),从而降低系统的氧化效率。然而,尽管碳酸盐物种会猝灭 HO,但在 UV/过碳酸钠(UV/SPC)中观察到 CO 对双酚 A(BPA)的降解有贡献。为了研究 UV/SPC 对 BPA 降解的性能以及 CO 在该过程中的作用,在等效 HO 浓度下比较了 UV/SPC 和 UV/过氧化氢(UV/HO)中 BPA 的降解动力学和机制。在这项研究中,UV/SPC 和 UV/HO 在 Milli-Q 水中对 BPA 的降解速率相似。在自由基猝灭剂叔丁醇和苯酚存在的情况下,BPA 降解速率的变化表明 CO 和 HO 都有助于 UV/SPC 中 BPA 的降解。CO 对 BPA 的二级反应速率常数( [Formula: see text] = 2.23 × 10 M s)和 UV/SPC 中的 CO 稳态浓度( [Formula: see text] = 2.3 × 10 M)和 HO( [Formula: see text] = 1.82 × 10 M)在 1 mM SPC 和 pH 8.5 下通过竞争动力学确定。在 UV/SPC 中观察到的高 [Formula: see text] 补偿了与 [Formula: see text] 相比较小的 [Formula: see text] 以及 HO 的消耗,使 BPA 在 UV/SPC 中的降解速率与在 UV/HO 中的降解速率相当。在 UV/SPC 中对 BPA 的转化产物(TPs)进行的详细研究表明,苯酚环和亚异丙基桥是 BPA 的主要反应位点。相应地提出了降解途径。动力学和机理研究的结果提供了对 UV/SPC 中 BPA 降解的更好的基本理解,以及 HCO&CO 对 HO-AOPs 中 BPA 降解的影响。这也证明了基于 CO 的水净化技术的潜力。