The Fenton reaction (H 2 O 2 +Fe 2 + /Fe 3 + ) has been widely used to oxidize organic compounds for various purposes, such as DNA damage by free radicals, [1] organic or inorganic synthesis, [2] and environmental detoxication. [3] As a versatile catalysis system, Fenton-like reactions have particular features: readily available and inexpensive reagents, extremely large rate constants (ca. 10 9 m À1 s À1 ), and a facile procedure. [4] The generally accepted free-radical-chain mechanism for the Fenton reactions is shown below, [5] and the slow reaction [Eq.(2)] is the rate-determining step.When Fenton reactions are used for rebating organic pollutants in water, if the cycle of iron species is not fast enough, or furthermore is not sustainable, the degradation rate and mineralization yield of pollutants would be very low and low-molecular-weight organic acids accumulate unavoidably during the degradation of organic substrates, thereby leading to the complete impedance of the whole reaction. [6] The acceleration of iron cycling and the more-efficient production of powerful HO· (E 0 = + +2.59 V vs. NHE; NHE = normal hydrogen electrode) as reactive species, to oxidize substrates in this chemical system, have become challenging goals for advanced oxidation processes (AOPs).In recent decades, the Fenton-like chemistry based on iron complexes of N-donor ligands has made a giant step towards significant acceleration of iron cycling. [7] Meunier and co-workers [7a] and Collins and co-workers [7b] have developed catalysts that use special iron complexes in the place of free Fe 2 + or Fe 3 + ions. These intricate catalysts resemble enzymes to some extent and show high catalytic activities for the degradation of organic pollutants. However, for the former, having an acetonitrile co-solvent in water as an axial ligand for the FePcS catalyst is needed; for the latter, the Fe-TAML catalyst is itself oxidatively degraded during recyclable use and even de-metalates in some standard buffers. [8] Our group has also reported some iron complexes that can activate H 2 O 2 under visible-light irradiation to effectively degrade organic pollutants in water without any co-solvent, albeit with relatively low activity. [9] Recently, an interesting study into attenuation of the Fenton reaction by iron chelation was reported, which is the reverse strategy to the above efforts for inhibiting oxidative stress; [10] moreover, tuning the Fenton-like reaction to inhibit or induce oxidative stress by UV-light-activated release of caged copper from a photolabile ligand was also reported. [11] Fenton reactions can be accelerated by UV-light illumination [3b, 12] but not by much-broader visible-light irradiation. This feature is because the absorption wavelength of Fe(OH) 2 + is less than 400 nm and general organic pollutants cannot absorb visible light. Visible-light irradiation comprises about 50 % of the sun's energy, and thus using visible light to accelerate the Fenton-like reactions is strongly desirable but remains a challenge. Herein, w...