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Two advanced oxidation pathways of modified iron-shavings participation in ozonation

机译:改良铁刨花的两种先进的氧化途径参与臭氧

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摘要

In this study, the performance of ozonation, catalytic ozonation and activation of molecular oxygen (AMO) process was examined with oxalate as the target refractory organics. Modified iron-shavings was used as catalyst for catalytic ozonation in degradation of oxalate at ambient temperature (25 +/- 2 degrees C). Under catalytic ozonation, the removal of oxalate was as high as 90%, which was much better than ozone alone. Initial pH was a key factor affecting the mechanisms of oxalate degradation. In AMO process, with the existence of Fe (II) there occurred an inner-Fenton reaction, hydrogen peroxide (H2O2) was produced at initial pH2.27 and its concentration ranged from 120 to 200 mu mol/L. Heterogeneous catalytic ozonation occurred in alkaline solution with hydroxyl radicals (center dot OH) production, which was indirectly oxidation instead of inner-Fenton reaction. Carbonate would be produced in alkaline solution during catalytic ozonation of oxalate which would in turn inhibit the process. Lepidocrocite (gamma-FeOOH) was formed through the dissolved iron ions precipitation and considered as the main component of catalyst, which was confirmed via field emission scanning electron microscope with energy-dispersive spectrometer (SEM-EDS), X-ray powder diffraction (XRD) and X-ray photoelectron spectroscopy (XPS). Hydroxyl radicals produced via different paths were detected out by electron paramagnetic resonance (EPR) and were considered as strong oxidant in catalytic ozonation and AMO process.
机译:在该研究中,用草酸盐作为目标耐火物质检查臭氧化,催化臭氧化和分子氧气(AMO)过程的活化的性能。在环境温度(25 +/- 2℃)下,改性的铁刨花用作催化臭氧化的催化臭氧化合物的催化剂(25 +/- 2℃)。在催化臭氧化下,将草酸盐的除去高达90%,其单独的臭氧要好得多。初始pH是影响草酸盐降解机制的关键因素。在amo工艺中,随着Fe(II)的存在,发生了内部芬顿反应,在初始pH2.27中产生过氧化氢(H 2 O 2),其浓度范围为120至200μmmol/ l。异质催化臭氧化发生在碱性溶液中,羟基溶液(中心点OH)产生,其间接氧化而不是内芬顿反应。在草酸盐的催化臭氧过程中,碳酸盐将在碱性溶液中产生,这反过来又抑制该过程。通过溶解的铁离子沉淀形成鳞片(Gamma-FeOOH),并被认为是催化剂的主要成分,通过现场发射扫描电子显微镜通过具有能量分散光谱仪(SEM-EDS),X射线粉衍射(XRD )和X射线光电子能量谱(XPS)。通过电子顺磁共振(EPR)检测通过不同路径产生的羟基自由基,被认为是催化臭氧化和AMO工艺中的强氧化剂。

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