Li Luwei, Qian Xuecong, Wang Shilong, Liu Yun, Wang Da, Zhang Huixin, An Yechen, Cheng Haijun, Ma Jun
State Key Laboratory of Urban Water Resource and Environment, School of Environment, Harbin Institute of Technology, Harbin 150090, China.
Key Laboratory of Microbial Technology for Industrial Pollution Control of Zhejiang Province, College of Environment, Zhejiang University of Technology, Hangzhou 310032, China.
J Hazard Mater. 2025 Sep 5;495:139014. doi: 10.1016/j.jhazmat.2025.139014. Epub 2025 Jun 25.
While non-radical Co species are recognized as critical intermediates in peroxymonosulfate (PMS)/Co(II) systems, their speciation and formation pathways remain under debate. In this study, Mn(II), characterized by well-defined redox behavior and mild reactivity toward radical species, was employed as a mechanistic probe to elucidate the activation mechanism of the PMS/Co(II) system under near-neutral conditions. Trace Co(II) (1 µM) accelerated Mn(II) oxidation kinetics by over 2000-fold at pH 8.0 compared to PMS alone. Scavenging experiments and near-100 % PMS utilization efficiency confirmed a non-radical mechanism. Co(IV) was proposed as the primary reactive species. Mn(III) capture experiments and density functional theory calculations indicated that Co(IV) oxidized Mn(II) via single-electron transfer. The derived Co(III) byproduct further contributed to Mn(II) oxidation, with reaction rates of 1.06 × 10 M·s at pH 5.5 and 1.20 × 10 M·s at pH 8.0. Kinetic modeling validated this pathway, quantifying the Co(IV)-Mn(II) reaction rates as 2.88 × 10 M·s (pH 5.5) and 2.57 × 10 M·s (pH 8.0). Under the experimental conditions, Co(III) and Co(IV) contributed comparably to Mn(II) oxidation. Mn(II)-probing experiments revealed that organic contaminant degradation was governed by substrate-dependent competition among three key reactive species: Co(II)-PMS complexes, high-valent cobalt species, and radicals. These findings provided mechanistic insights into PMS/Co(II) activation and further confirmed its potential for efficient manganese removal in water treatment.
虽然非自由基态的钴物种被认为是过一硫酸盐(PMS)/Co(II)体系中的关键中间体,但其形态和形成途径仍存在争议。在本研究中,以具有明确氧化还原行为且对自由基物种反应活性温和的Mn(II)作为机理探针,以阐明近中性条件下PMS/Co(II)体系的活化机制。与单独的PMS相比,痕量Co(II)(1 µM)在pH 8.0时将Mn(II)氧化动力学加速了2000多倍。清除实验和近100%的PMS利用效率证实了非自由基机制。Co(IV)被认为是主要的活性物种。Mn(III)捕获实验和密度泛函理论计算表明,Co(IV)通过单电子转移氧化Mn(II)。衍生的Co(III)副产物进一步促进了Mn(II)的氧化,在pH 5.5时反应速率为1.06×10 M·s,在pH 8.0时反应速率为1.20×10 M·s。动力学模型验证了该途径,将Co(IV)-Mn(II)反应速率量化为2.88×10 M·s(pH 5.5)和2.57×10 M·s(pH 8.0)。在实验条件下,Co(III)和Co(IV)对Mn(II)氧化的贡献相当。Mn(II)探测实验表明,有机污染物的降解受三种关键活性物种之间底物依赖性竞争的控制:Co(II)-PMS络合物、高价钴物种和自由基。这些发现为PMS/Co(II)活化提供了机理见解,并进一步证实了其在水处理中高效去除锰的潜力。