Low-concentration organic pollutants (e.g., antibiotics) challenge conventional Fenton oxidation due to slow kinetics and matrix interference. Herein, a Cu-doped natural iron-containing attapulgite (Cu-ATP) with dual Fe-Cu active sites was developed for synergistic adsorption and in situ Fenton-like oxidation. The optimized Cu-ATP 2/3 exhibited a high adsorption capacity (96.36 mg g-1) toward tetracycline hydrochloride (TCH) and enhanced oxidation kinetics (apparent rate constant: 0.0143 min-1), outperforming many reported metallic catalysts. Mechanistic results indicate that Cu incorporation improves the mesoporous structure for pollutant enrichment and promotes the Fe(III)/Fe(II) redox cycle via electronic modulation. Meanwhile, the Cu(II)/Cu(I) cycle, driven by H2O2 and •O2H, sustains catalytic activity, while •OH adsorbed on the surface achieves in situ Fenton oxidation of pollutants. The Cu-ATP/H2O2 system operates over a wide pH range (3.3-9.7) and shows strong resistance to coexisting ions (e.g., Cl-, NO3-, SO42-, and H2PO4-) and humic acid. Continuous fixed-bed experiments demonstrated stable TCH removal (>85% over 250 L) with negligible metal leaching (-1). This work establishes a Cu-enhanced dual-site redox cycle strategy for coupled adsorption-oxidation, offering actionable mechanistic insights for designing high-efficiency, sustainable catalysts and underscoring the practical viability of integrated adsorption-oxidation systems for real wastewater remediation.
Jiang et al. (2026) studied this question.