Department of Environmental Engineering, Faculty of Civil Engineering, Istanbul Technical University Istanbul, Turkey.
Front Chem. 2013 Mar 20;1:4. doi: 10.3389/fchem.2013.00004. eCollection 2013.
This study explored the potential use of a sulfate radical (SO(·-) 4)-based photochemical oxidation process to treat the commercial nonionic surfactant octylphenol polyethoxylate (OPPE) Triton™ X-45. For this purpose, the effect of initial S2O(2-) 8 (0-5.0 mM) and OPPE (10-100 mg/L) concentrations on OPPE and its organic carbon content (TOC) removal were investigated at an initial reaction pH of 6.5. Results indicated that very fast OPPE degradation (100%) accompanied with high TOC abatement rates (90%) could be achieved for 10 and 20 mg/L aqueous OPPE at elevated S2O(2-) 8 concentrations (≥2.5 mM). S2O(2-) 8/UV-C treatment was still capable of complete OPPE removal up to an initial concentration of 40 mg/L in the presence of 2.5 mM S2O(2-) 8. On the other hand, TOC removal efficiencies dropped down to only 40% under the same reaction conditions. S2O(2-) 8/UV-C oxidation of OPPE was also compared with the relatively well-known and established H2O2/UV-C oxidation process. Treatment results showed that the performance of S2O(2-) 8/UV-C was comparable to that of H2O2/UV-C oxidation for the degradation and mineralization of OPPE. In order to elucidate the relative reactivity and selectivity of SO(·-) 4 and HO(·), bimolecular reaction rate coefficients of OPPE with SO(·-) 4 and HO(·) were determined by employing competition kinetics with aqueous phenol (47 μM) selected as the reference compound. The pseudo-first-order abatement rate coefficient obtained for OPPE during S2O(2-) 8/UV-C oxidation (0.044 min(-1)) was found to be significantly lower than that calculated for phenol (0.397 min(-1)). In the case of H2O2/UV-C oxidation however, similar pseudo-first-order abatement rate coefficients were obtained for both OPPE (0.087 min(-1)) and phenol (0.140 min(-1)). From the kinetic study, second-order reaction rate coefficients for OPPE with SO(·-) 4 and HO(·) were determined as 9.8 × 10(8) M(-1) s(-1) and 4.1 × 10(9) M(-1) s(-1), respectively. The kinetic study also revealed that the selectivity of SO(·-) 4 was found to be significantly higher than that of HO(·).
本研究探索了基于硫酸根自由基(SO(·-) 4)的光化学氧化工艺处理商业非离子表面活性剂辛基酚聚氧乙烯醚(OPPE)Triton™ X-45 的潜力。为此,在初始反应 pH 值为 6.5 的条件下,研究了初始 S2O(2-) 8(0-5.0 mM)和 OPPE(10-100 mg/L)浓度对 OPPE 及其有机碳含量(TOC)去除的影响。结果表明,在升高的 S2O(2-) 8 浓度(≥2.5 mM)下,10 和 20 mg/L 水溶液 OPPE 可实现非常快速的 OPPE 降解(100%)和高 TOC 去除率(90%)。在 2.5 mM S2O(2-) 8 的存在下,S2O(2-) 8/UV-C 处理仍能够完全去除初始浓度高达 40 mg/L 的 OPPE。另一方面,在相同的反应条件下,TOC 去除效率下降到仅 40%。S2O(2-) 8/UV-C 氧化 OPPE 也与相对知名和成熟的 H2O2/UV-C 氧化过程进行了比较。处理结果表明,S2O(2-) 8/UV-C 的性能与 H2O2/UV-C 氧化相当,可用于 OPPE 的降解和矿化。为了阐明 SO(·-) 4 和 HO(·)的相对反应性和选择性,通过采用竞争动力学,用选定的 47 μM 水溶液苯酚作为参比化合物,确定了 OPPE 与 SO(·-) 4 和 HO(·)的双分子反应速率系数。在 S2O(2-) 8/UV-C 氧化过程中,OPPE 的假一级衰减速率系数(0.044 min(-1)))发现明显低于计算得到的苯酚(0.397 min(-1)))。然而,在 H2O2/UV-C 氧化的情况下,OPPE(0.087 min(-1)))和苯酚(0.140 min(-1)))的假一级衰减速率系数则非常相似。从动力学研究中,确定了 OPPE 与 SO(·-) 4 和 HO(·)的二级反应速率系数分别为 9.8×10(8) M(-1) s(-1)和 4.1×10(9) M(-1) s(-1)。动力学研究还表明,SO(·-) 4 的选择性明显高于 HO(·)。