Radical-dependent advanced oxidation processes (AOPs) have emerged as promising technologies for water decontamination, yet remain constrained by critical limitations, including susceptibility to matrix quenching and the formation of toxic byproducts, which hinder their broad application. To address these challenges, this study engineers a ligand-stabilized permanganate/sulfite (Mn(VII)/S(IV)) system using nitrilotriacetic acid (NTA) for efficient degradation of recalcitrant organic pollutants across a wide pH range. The NTA coordination critically stabilizes reactive Mn intermediates (Mn(III) and Mn(V)), generated via two-electron reduction of Mn(VII) by S(IV), effectively mitigating their deactivation through hydrolysis or disproportionation at near-neutral pH. This stabilization enables sustained catalytic activity from pH 4–7.5, overcoming the strict acidic pH requirement of conventional Mn(VII)/S(IV) systems. Mechanistic investigations reveal dual oxidation pathways: Mn(III)–NTA species mediate radical-based oxidation through SO4•− generation, while Mn(V)−NTA species dominate non-radical two-electron oxidation process. Crucially, the Mn(VII)/S(IV) molar ratio serves as a tunable lever governing oxidation pathway selection: higher ratios favor non-radical Mn(V)−NTA oxidation, whereas lower ratios promote SO4•−-based pathways that are subject to self-quenching by excess S(IV). Dissolved oxygen further sustains the catalytic cycles by preventing premature Mn(V) reduction and facilitating oxysulfur radical chain propagation. Moreover, the NTA coordination confers exceptional resilience against common water matrix interferents (e.g., anions and natural organic maters), while maintaining high degradation efficacy in diverse natural waters. This work demonstrates that ligand-stabilized high-valent Mn(V) catalysis enables tunable and robust oxidation pathways, providing new mechanistic insights for precision oxidation technologies.


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