State Key Laboratory of Hydraulics and Mountain River Engineering, College of Architecture and Environment, Sichuan University, Chengdu 610065, China; School of Chemical Engineering, The University of Adelaide, Adelaide, SA 5005, Australia; Sino-German Centre for Water and Health Research, Sichuan University, Chengdu 610065, China.
State Key Laboratory of Hydraulics and Mountain River Engineering, College of Architecture and Environment, Sichuan University, Chengdu 610065, China; Sino-German Centre for Water and Health Research, Sichuan University, Chengdu 610065, China.
Water Res. 2024 Jun 15;257:121715. doi: 10.1016/j.watres.2024.121715. Epub 2024 May 2.
High-valent metal-oxo species (HMOS) have been extensively recognized in advanced oxidation processes (AOPs) owing to their high selectivity and high chemical utilization efficiency. However, the interactions between HMOS and halide ions in sewage wastewater are complicated, leading to ongoing debates on the intrinsic reactive species and impacts on remediation. Herein, we prepared three typical HMOS, including Fe(IV), Mn(V)-nitrilotriacetic acid complex (Mn(V)NTA) and Co(IV) through peroxymonosulfate (PMS) activation and comparatively studied their interactions with Cl to reveal different reactive chlorine species (RCS) and the effects of HMOS types on RCS generation pathways. Our results show that the presence of Cl alters the cleavage behavior of the peroxide OO bond in PMS and prohibits the generation of Fe(IV), spontaneously promoting SO production and its subsequent transformation to secondary radicals like Cl and Cl. The generation and oxidation capacity of Mn(V)NTA was scarcely influenced by Cl, while Cl would substantially consume Co(IV) and promote HOCl generation through an oxygen-transfer reaction, evidenced by density functional theory (DFT) and deuterium oxide solvent exchange experiment. The two-electron-transfer standard redox potentials of Fe(IV), Mn(V)NTA and Co(IV) were calculated as 2.43, 2.55 and 2.85 V, respectively. Due to the different reactive species and pathways in the presence of Cl, the amounts of chlorinated by-products followed the order of Co(II)/PMS > Fe(II)/PMS > Mn(II)NTA/PMS. Thus, this work renovates the knowledge of halide chemistry in HMOS-based systems and sheds light on the impact on the treatment of salinity-containing wastewater.
高价金属氧物种 (HMOS) 因其高选择性和高化学利用效率而在高级氧化工艺 (AOPs) 中得到广泛认可。然而,HMOS 与污水废水中卤化物离子之间的相互作用很复杂,这导致关于固有反应性物种及其对修复影响的争论仍在继续。在此,我们通过过一硫酸盐 (PMS) 活化制备了三种典型的 HMOS,包括 Fe(IV)、Mn(V)- 氮三乙酸络合物 (Mn(V)NTA) 和 Co(IV),并比较研究了它们与 Cl 的相互作用,以揭示不同的活性氯物种 (RCS) 以及 HMOS 类型对 RCS 生成途径的影响。我们的结果表明,Cl 的存在改变了 PMS 中过氧 OO 键的断裂行为,阻止了 Fe(IV)的生成,自发促进 SO 的生成及其随后转化为 Cl 和 Cl 等次级自由基。Cl 的存在对 Mn(V)NTA 的生成和氧化能力影响不大,而 Cl 会通过氧转移反应大量消耗 Co(IV)并促进 HOCl 的生成,这一点可以通过密度泛函理论 (DFT) 和重水溶剂交换实验得到证明。Fe(IV)、Mn(V)NTA 和 Co(IV)的两电子转移标准氧化还原电位分别计算为 2.43、2.55 和 2.85 V。由于 Cl 的存在会导致不同的反应性物种和途径,氯化副产物的生成量遵循 Co(II)/PMS > Fe(II)/PMS > Mn(II)NTA/PMS 的顺序。因此,这项工作更新了关于 HMOS 基体系中卤化物化学的知识,并阐明了其对含盐废水处理的影响。