Copper-iron oxides exhibit distinct Fenton-like degradation properties towards different pollutants, but the underlying mechanisms for these differences remain unclear. To address this knowledge gap, the selective Fenton-like processes were investigated using copper ferrite (CuFe2O4) as the catalyst. CuFe2O4 selectively degraded ciprofloxacin (CIP), with 50.2 % adsorption and 82.5 % degradation rates, significantly surpassing those of bisphenol A (BPA), 19.7 % and 38.2 %, respectively. Mechanistic studies indicated that the Fenton-like degradation by CuFe2O4 were mainly governed by catalyst adsorption capacity and reactive oxygen species production. The selective adsorption of CuFe2O4 towards CIP facilitated the electron transfer with H2O2. This process and 1O2 generated in the system were the primary factor contributing to the selective degradation. Degradation experiments with other pollutants confirmed the proposed mechanism. Additionally, increasing the Cu/Fe ratio in copper-iron oxides enhanced the production of ·OH and ·O2-, significantly improving the degradation and mineralization of CIP and BPA (e.g., at a Cu/Fe ratio of 1:0.6, the degradation efficiencies both exceeded 90 % in ultrapure water and reached around 80 % in real water systems), with radical oxidation as the dominant degradation pathway. This study proposes a strategy for selective pollutant degradation by modifying catalyst composition, aiding targeted Fenton-like system development for water treatment.
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