Chemical oxidation, typified by Fenton and Fenton-like reactions, is a widely adopted and promising wastewater treatment technology, known for its ability to produce highly reactive oxide species that efficiently remove pollutants [
1-
3]. However, this process typically demands significant energy/chemical agent input to mineralize organic pollutants, converting the carbon within them into CO
2. This results in the loss of a substantial amount of chemical energy contained in the wastewater, making energy recovery quite challenging [
4]. Developing approaches to regulate the oxidation pathway of pollutant from mineralization to polymerization is a crucial step in advancing water treatment from pollution control to energy recovery, ultimately reducing the carbon footprint. Direct surface oxidation of the pollutants by forming oligomers is a potential way to regulate the polymerization pathway. Elimelech and co-workers [
5,
6] have demonstrated that the surface of high valence metal oxides can initiate surface-dependent coupling and polymerization pathways for the removal of organic compounds
via a two-electron direct oxidation process. Specifically, oxidant activation and organic adsorption occur simultaneously at adjacent sites on the catalyst surface, followed by the creation of positively charged centers on neighboring and pairs of carbon atoms in the phenolic hydroxyl group of the organics, leading to C—C coupling or spontaneous C—O polymerization of the stabilized phenoxonium ions. Three crucial functions of the nanocatalyst surface,
i.e., activation, stabilization and accumulation were revealed to render the direct oxidation process thermodynamically spontaneous and kinetically favorable. Except for such direct surface oxidation process, recent studies highlighted that spatial nanoconfinement can substantially alter the thermodynamic and kinetic behaviors of chemical reactions, leading to different reaction pathways and outcomes compared to the bulk oxidation reaction [
7]. Spatial nanoconfinement can trigger thermodynamically favorable oligomerization routes for the removal of organic pollutants, due to its more negative Gibbs free energy compared to the open-ring route [
8,
9]. Under spatial nanoconfinement, the oxidant exhibits higher adsorption energy and lower activation energy barriers on the catalyst. This facilitates the breaking of O—O or C—O bonds in the oxidants and enhances electron migration from the molecular orbitals of the metal particles, thereby activating the oxidants more easily. Additionally, spatial nanoconfinement triggers synergistic effects such as reactant enrichment, electron-metal-carrier interactions, and improved mass transfer. These effect will increase the localized reactant concentration, which is considered kinetically favorable [
10,
11]. The local enrichment of reactants at high concentrations promotes effective molecular collisions, shortens the mass transfer distance of ROS and facilitates efficient internal electron transfer, thus enhancing the removal of organic pollutants at higher reaction rates [
12]. This phenomenon holds promise for converting organic pollutant into polymers for recovery, thereby enabling green and low-carbon sewage and wastewater treatment [
8,
12,
13]. Nevertheless, more in-depth understanding of how nanoconfinement affects the oxidation pathway of pollutant is still lacking, and the potential mechanism underlying the selectivity enhancement of oligomers under nanoconfinement remains uncovered.