用于光催化降解活性橙 13 的新型淀粉改性镍铬锰-LDH 基复合材料

Catalysts Pub Date : 2024-07-12 DOI:10.3390/catal14070449
Muhammad Usman, M. Taj, A. Almasoudi, Doaa F. Baamer, Omar Makram Ali, Muhammad Imran Khan, I. Bibi, Mobeen Ur Rehman, R. Rasheed, A. Raheel, M. H. Lashari, Abdallah Shanableh, Javier Fernandez-Garcia
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引用次数: 0

摘要

水污染已成为当今的一大挑战。为了解决废水处理问题,去除废水中的有毒合成染料,本研究通过共沉淀法合成了新型淀粉改性镍铬锰双氢氧化物复合材料,并将其用作光催化剂降解活性橙 13 染料。通过 X 射线衍射 (XRD)、傅立叶变换红外光谱 (FTIR)、扫描电子显微镜 (SEM)、Brunauer-Emmett-Teller (BET)、零电荷点 (PZC)、动态光散射 (DLS)、热重分析 (TGA)、差示扫描量热 (DSC) 和 Zeta 电位技术对合成的光催化剂进行了表征。这些技术揭示了光催化剂的不同特性,如表面和结构特性。根据 BET 分析,最终复合材料的 BET 比表面积为 2.5 × 102 m2/g,孔半径值为 45.56 nm,整体复合材料为介孔。同样,在 DLS 分析中,裸 NiCrMn-LDH 的流体力学尺寸为 404 nm,而最终淀粉复合材料的流体力学尺寸增加到 667 nm。淀粉与 NiCrMn-LDH 结合后,Zeta 电位值从 -14.56 mV 变为 0.95 mV。他们证实了淀粉与三金属镍铬锰-层状双氢氧化物(2:1:2)的结合。淀粉的加入改善了光催化剂的特性,如表面积。研究了降解 RO13 的不同参数,如 pH 值、初始染料浓度、光催化剂剂量、过氧化氢浓度、牺牲试剂的影响以及无机阴离子的影响。总的来说,RO13 的光催化过程遵循伪一阶动力学。在初始染料浓度为 10 毫克/升、光催化剂用量为 20 毫克/50 毫升、pH 值为 3 且有阳光照射的条件下,对活性橙 13 进行了光催化降解反应,结果降解去除率高达 86.68%。光催化剂对活性橙 13 的出色降解能力证明了这种复合材料的高效性。
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Novel Starch-Modified NiCrMn-LDH-Based Composite for Photocatalytic Degradation of Reactive Orange 13
Water pollution has become a great challenge today. To address this problem regarding wastewater treatment by removing toxic synthetic dyes from wastewater, this research focused on the synthesis of a novel starch-modified NiCrMn-layered double hydroxide composite through the coprecipitation method and applied it as a photocatalyst for the degradation of reactive orange 13 dye. The synthesized photocatalyst was characterized by X-ray diffraction (XRD), Fourier transform infrared spectroscopy (FTIR), scanning electron microscopy (SEM), Brunauer–Emmett–Teller (BET), point of zero charges (PZC), dynamic light scattering (DLS), thermogravimetric analysis (TGA), differential scanning calorimetry (DSC) and Zeta potential techniques. These techniques revealed different characteristics of photocatalysts, like surface and structural properties. According to BET analysis, the final composite had 2.5 × 102 m2/g BET-specific surface area with a 45.56 nm pore radius value, and the overall composite found as mesoporous. Similarly, in DLS analysis, bare NiCrMn-LDH had 404 nm hydrodynamic size, which increased for the final starch composite up to 667 nm. Zeta potential value changed from −14.56 mV to 0.95 mV after the incorporation of starch with NiCrMn-LDH. They confirmed the incorporation of starch with trimetallic NiCrMn-layered double hydroxide (2:1:2). Starch association improved the properties of the photocatalyst like surface area. Different parameters like pH value, initial dye concentration, photocatalyst dose, hydrogen peroxide concentration, effect of sacrificial reagent, and effect of inorganic anions were studied for degradation of RO13. Overall, the photocatalysis process for RO13 followed pseudo-first-order kinetics. Photocatalytic degradation reactions for reactive orange 13 were conducted with an initial dye concentration of 10 mg/L, photocatalyst dosage of 20 mg/50 mL, and pH value at 3 in the presence of sunlight, resulting in an impressive degradation removal rate of 86.68%. This remarkable degradation ability of the photocatalyst for reactive orange 13 proves this composite was highly efficient.
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