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首页> 外文期刊>Catalysis Today >Hydroxylamine promoted Fe(III)/Fe(II) cycle on ilmenite surface to enhance persulfate catalytic activation and aqueous pharmaceutical ibuprofen degradation
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Hydroxylamine promoted Fe(III)/Fe(II) cycle on ilmenite surface to enhance persulfate catalytic activation and aqueous pharmaceutical ibuprofen degradation

机译:羟胺促进钛铁矿表面上的Fe(III)/ Fe(II)循环,以增强过硫酸盐催化活化和水性药物布洛芬降解

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摘要

This study demonstrates a new system for the degradation of emerging pharmaceutical contaminants (e.g., ibuprofen) in water by coupling the naturally occurring ilmenite with hydroxylamine (HA) and persulfate (PS). Ilmenite was able to activate persulfate to generate sulfate radicals (SO4-center dot) and hydroxyl radicals (HO center dot). The radical generation was greatly improved by adding small amount of hydroxylamine into the solution, due to the efficient Fe(III)/Fe(II) cycle on the ilmenite surface promoted by HA, which was confirmed by X-ray photoelectron spectroscopy and electron paramagnetic resonance (EPR) spectroscopy analysis. SO4-center dot and HO center dot contributed comparably to ibuprofen degradation, which was verified by the radical scavenging tests. The degradation was enhanced with increasing ilmenite, PS and HA dosages, but the HA exhibited strong scavenging effect at its high concentrations. The ilmenite/PS/HA process worked well in the real treated wastewater, because the surface-controlled radical generation was less affected by the water matrix. However, the formation of bromate in the bromide-containing water by this process should be concerned. Ibuprofen was partially mineralized, and the degradation products were identified by ESI-tqMS. A radical-induced degradation pathway was proposed based on the product identification. This work provides the mechanistic insights on persulfate activation based on the surface-controlled catalytic processes. It also offers a new strategy to degrade emerging contaminants in water and sheds light on the environmental functions of natural minerals.
机译:这项研究展示了一种通过将自然生成的钛铁矿与羟胺(HA)和过硫酸盐(PS)偶联来降解水中新出现的药物污染物(如布洛芬)的新系统。钛铁矿能够激活过硫酸盐生成硫酸根(SO4中心点)和羟基自由基(HO中心点)。通过向溶液中加入少量羟胺,自由基的生成得到了极大的改善,这是由于HA促进了钛铁矿表面的有效Fe(III)/Fe(II)循环,这一点已被X射线光电子能谱和电子顺磁共振(EPR)谱分析所证实。SO4中心点和HO中心点对布洛芬降解的贡献相当,这已通过自由基清除试验得到验证。随着钛铁矿、PS和HA用量的增加,降解增强,但HA在高浓度时表现出强烈的清除作用。钛铁矿/PS/HA工艺在实际处理的废水中运行良好,因为表面控制的自由基生成受水基质的影响较小。然而,应关注通过该工艺在含溴水中形成溴酸盐的情况。布洛芬部分矿化,降解产物经ESI-tqMS鉴定。在产物鉴定的基础上,提出了自由基诱导的降解途径。这项工作为基于表面控制催化过程的过硫酸盐活化提供了机理上的见解。它还提供了一种新的策略来降解水中新出现的污染物,并揭示了天然矿物的环境功能。

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