Abstract
In this study, compounding Fe@Fe2O3 with humic acid (HA) enhanced peroxymonosulfate (PMS) activation to degrade 2,4,6-trichlorophenol (TCP). The characterization and catalytic performance of the materials revealed that Fe@Fe2O3-HA had more functional groups, more surface oxygen vacancies, higher stability, and higher cyclicality. HA promoted the continuous release of iron ions as well as the process of PMS activation by accelerating Fe3+ reduction. The results of electron paramagnetic resonance (EPR) and quenching experiments indicated that more reactive oxygen species (ROS) were generated in the Fe@Fe2O3-HA/Fe2+/PMS system, and SO4− was the dominant ROS for TCP degradation. The degradation efficiency of TCP in the Fe@Fe2O3/Fe2+/PMS system was increased from 59% to 83% within 10 min after HA was compounded. The degradation efficiency of TCP in the Fe@Fe2O3-HA/Fe2+/PMS system was greatest at 60 min under alkaline conditions. Thus, our results demonstrated that Fe@Fe2O3-HA, a highly active catalyst exhibited excellent reactivity in the potential application of Fe2+/PMS for groundwater protection.
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