In this study, Fe@Fe 2 O 3 core−shell nanowires were first used as a novel Fenton iron reagent. The nanowires were synthesized through the reduction of ferric chloride aqueous solution by sodium borohydride at ambient atmosphere, without protection of inert gases or vacuum. Rhodamine B (RhB) could be efficiently degraded in aqueous media by a novel sonochemical-assisted Fenton (sono-Fenton) system based on these Fe@Fe 2 O 3 core−shell nanowires. The RhB degradation processes were monitored by UV−vis spectroscopy and total organic carbon (TOC) analysis. Fe@Fe 2 O 3 core−shell nanowires showed much higher activity in the sono-Fenton system than other iron reagents such as commercial zerovalent iron powders (Fe 0 ), ferrous ions (Fe 2+ ), and ferric ions (Fe 3+ ). It was found that near 100% decoloration and over 60% TOC removal of RhB (5 mg·L -1 ) could be achieved in 60 min by this novel sono-Fenton system with 0.018 mol·L -1 Fe@Fe 2 O 3 core−shell nanowires. This new iron reagents before and after the sono-Fenton reaction were examined by X-ray diffraction (XRD), scanning electron microscopy (SEM), and transmission electron microscopy (TEM). The characterizations found that the nanowires were transferred to nanotubes/nanoparticles covered with Fe 3 O 4 /Fe 2 O 3 after the sono-Fenton process. A possible mechanism of sono-Fenton degradation of RhB with Fe@Fe 2 O 3 nanowires was proposed on the basis of the experimental results. It involved homogeneous Fenton and heterogeneous Fenton oxidative degradation simultaneously. The high activity of core−shell Fe@Fe 2 O 3 nanowires and the success of their mass production make them attractive for the treatment of organic pollutants in water.
No takes yet. Share an insight, caveat, or question.
Ai et al. (2007) studied this question.
Synapse has enriched 5 closely related papers on similar clinical questions. Consider them for comparative context: