Abstract
Peroxymonosulfate (PMS)-based advanced oxidation processes often suffer from unstable activation and low mineralization efficiency when treating sulfamethoxazole (SMX). Herein, a magnetic pyrite–biochar (600MRSC1) derived from reed straw and pyrite was synthesized and implemented in a sequential non-radical–radical pathway (SNRP) system. The SNRP-600MRSC1/PMS system rapidly rapidly achieved near-complete SMX removal (>99%, within the detection limit) and a total organic carbon reduction of 72.8%, which was 2.17 times higher than that of the 600MRSC1/PMS system. Mechanistic investigations revealed that PMS degraded SMX via hydroxylation in Stage 1, while the resulting intermediates were further mineralized in Stage 2 by radicals generated from PMS activation by 600MRSC1, mainly SO4·- (41.22%) and ·OH (32.06%). The presence of S(II) promoted the generation of low-valent Fe species and accelerated Fe (II)/Fe (III) cycling, ensuring stable catalytic activity. The system also achieved complete SMX removal in tap and river water and maintained stable performance in five-cycle reuse experiments, showing strong applicability in real water matrices. This work provides a biochar-based strategy for improving PMS activation stability and achieving deep mineralization of organic pollutants.
| Original language | English |
|---|---|
| Article number | 129061 |
| Journal | Journal of Environmental Management |
| Volume | 402 |
| DOIs | |
| State | Published - 15 Mar 2026 |
Keywords
- Degradation
- Mineralization
- PMS
- Sulfamethoxazole
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