Removal of trichloroethene by glucose oxidase immobilized on magnetite nanoparticles

To overcome the safety risks and low utilization efficiency of H2O2 in traditional Fenton processes, in situ production of H2O2 by enzymatic reactions has attracted increasing attention recently. In this study, magnetite-immobilized glucose oxidase (MIG) was prepared to catalyze the heterogeneous Fenton reaction for the removal of trichloroethene from water. The successful immobilization of glucose oxidase on magnetite was achieved with a loading efficiency of 70.54%. When combined with substrate glucose, MIG could efficiently remove 5-50 mg L-1 trichloroethene from water with a final removal efficiency of 76.2% to 94.1% by 192 h. This system remained effective in the temperature range of 15-45 degrees C and pH range of 3.6-9.0. The removal was slightly inhibited by different cations and anions (influencing degree Ca2+ > Mg2+ > Cu2+ and H2PO4- > Cl- > SO42-) and humic acid. Meanwhile, the MIG could be recycled for 4 cycles and was applicable to other chlorinated hydrocarbons. The results of reactive oxidative species generation monitoring and quenching experiments indicated that H2O2 generated by the enzymatic reaction was almost completely decomposed by magnetite to produce center dot OH with a final cumulative concentration of 129 mu M, which played a predominant role in trichloroethene degradation. Trichloroethene was almost completely dechlorinated into Cl-, CO2 and H2O without production of any detectable organic chlorinated intermediates. This work reveals the potential of immobilized enzymes for in situ generation of ROS and remediation of organic chlorinated contaminants.

Automated summary

To address the safety risks and low utilization efficiency of H2O2 in traditional Fenton processes, researchers have turned to in situ production of H2O2 through enzymatic reactions. In this study, magnetite-immobilized glucose oxidase (MIG) was prepared and used for the heterogeneous Fenton reaction to remove trichloroethene from water. The MIG system exhibited high removal efficiency and remained effective across a wide range of temperature and pH conditions, with slight inhibition by certain cations, anions, and humic acid. The immobilized enzymes showed potential for in situ generation of reactive oxidative species and remediation of organic chlorinated contaminants.