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首页> 外文期刊>Chemical Engineering Communications >Catalytic ozonation process using PAC/gamma-Fe2O3 to Alizarin Red S degradation from aqueous solutions: a batch study
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Catalytic ozonation process using PAC/gamma-Fe2O3 to Alizarin Red S degradation from aqueous solutions: a batch study

机译:使用PAC / GAMMA-FE2O3与水溶液中的茜素红S降解的催化臭氧处理方法:批量研究

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In the catalytic ozonation process used in this study, adsorption and chemical reactions were performed at the catalyst surface. This process can increase the efficiency of plain ozonation. The main aim of this study was to investigate the efficiency of the catalytic ozonation process in removing Alizarin Red S dye from colored water by Fe2O3 coated on PAC. In this work, activated carbon powder/gamma-Fe2O3 nano-composite was modified. The BET results showed that the surface area in PAC and PAC-gamma-Fe2O3 nano-composite was 654 and 450 m(2) g(-1), respectively. In this study, the best pH for removal of ARS was found to be 9. At a higher pH, the efficiency of the process decreased gradually. According to studies, catalysts increase surface area and active sites for more ozone degradation. Also, the characterization of the catalyst will play a very important role in the COP. Also, the maximum removal efficiency was observed in catalyst dose 1.1 g l(-1). The study results showed that the highest mineralization rate in ARS degradation was related to O-3/PAC/gamma-Fe2O3. The amount of mineralization in the SOP, O-3-PAC, and O-3/PAC/gamma-Fe2O3 was 13, 25, and 40%, respectively. The finding of mineralization of ARS using the SOP reflected the low power of the ozonation process for the mineralization of pollutants.
机译:在本研究中使用的催化臭氧化过程中,在催化剂表面进行吸附和化学反应。这个过程可以提高普通臭氧化的效率。本研究的主要目的是探讨催化臭氧化方法在PAC上涂覆的Fe2O3从有色水中取出茜素红S染料的效率。在这项工作中,改性活性炭粉/γ-Fe 2 O 3纳米复合材料。 BET结果表明,PAC和PAC-GAMMA-FE2O3纳米复合材料中的表面积分别为654和450m(2 )g(-1)。在这项研究中,发现用于去除ARS的最佳pH为9。在较高的pH下,该过程的效率逐渐降低。根据研究,催化剂增加表面积和活性位点以获得更多臭氧的降解。而且,催化剂的表征将在警察中发挥非常重要的作用。此外,在催化剂剂量1.1g L(-1)中观察到最大去除效率。研究结果表明,ARS降解中的最高矿化率与O-3 / PAC /γ-Fe2O3有关。 SOP,O-3-PAC和O-3 / PAC /γ-Fe 2 O 3中的矿化量分别为13,25和40%。使用SOP的ARS矿化的发现反映了污染物矿化的臭氧化过程的低功率。

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