增强 MIL-53 (Fe)的结晶度并提高 MIL-53 (Fe) 在 TiO2 存在下对 Pb2+ 离子的去除率

Perera H.A.I.R., Warnapura A.G.S.M.
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引用次数: 0

摘要

由于各种污染物处理不当造成的水污染是全世界生物面临的最严重威胁之一。铅(Pb)是一种重金属,通常被电池制造、油漆等行业添加到环境中。根据世界卫生组织的数据,人体可承受的最大铅浓度为 70 μg dL-1。因此,有效去除受污染水中的重金属至关重要。在现有的各种去除技术中,吸附技术因其高效、低成本和易于设计而发挥着重要作用。MOFs 是一类结晶多孔吸附材料,由金属离子/团簇和有机连接体组成。由于其定制能力、高孔隙率和高表面积,它们已被广泛用于去除废水中的污染物。本研究的主要目的是合成 MIL-53 (Fe) MOF 和 MIL-53/TiO2 复合材料,并测定其在光照和黑暗条件下对铅(II)的去除效率。MIL-53 (Fe) MOF 是用铁(III)和 1,4-二羧酸在溶热条件下合成的。复合材料也是在有 TiO2 纳米颗粒存在的情况下合成的。粉末 X 射线衍射和傅立叶变换红外光谱证实了 MIL-53 (Fe) MOF 和 MOF/TiO 复合材料的成功合成。根据 Debye-Scherrer 方程,MOF 和 MOF/TiO22 复合材料的晶粒大小分别为 79.06 nm 和 65.46 nm。原子吸收光谱用于测定吸附前后的金属离子浓度。两种吸附剂在光照和黑暗条件下去除铅(II)的最佳条件分别为:初始铅离子浓度分别为 50 mg L-1 和 25 mg L-1,吸附剂剂量分别为 10 mg 和 12.5 mg(对于 25 ml 50 mg L-1 的铅(II)),接触时间分别为 90 分钟和 90 分钟。溶液的 pH 值保持在中性水平,以确保去除污染物后废水的可再利用性。两种吸附剂的吸附等温线都与 Langmuir 模型十分吻合,表明它们都是单层吸附。因此,在 pH 值为 7 时,MOF 和 MOF/TiO2 复合材料分别获得了 396.35 mg g-1 和 786.16 mg g-1 的最大铅(II)吸附容量。因此,与 MOF 相比,复合材料对铅(II)离子的去除率明显提高。 关键词吸附 重金属 等温线 MIL-53 (Fe)
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Enhanced Crystallinity of MIL-53 (Fe) and Improved Pb2+ Ion Removal by MIL-53(Fe) in the Presence of TiO2
Water pollution due to improper disposal of various contaminants is one of the most serious threats faced by living beings all around the world. Lead (Pb) is a heavy metal which is commonly added to the environment by the industries such as battery manufacturing, paints etc. According to the world health organization, the maximum bearable Pb concentration of the human body is 70 μg dL- 1. However, in a contaminated water sample, this value could range from 200 to 500 mg L-1. Thus, the efficient removal of heavy metals from contaminated water is vital. Among various removal techniques available, adsorption plays a major role due to its high efficiency, low cost and ease of designing. MOFs are a class of crystalline porous adsorbent material that consists of a metal ion/cluster and an organic linker. Owing to their tailoring ability, high porosity, and high surface area they have been widely used in the removal of contaminants from wastewater. The main objectives of this study are to synthesize MIL-53 (Fe) MOF and MIL-53/TiO2 composite and determine the Pb (II) removal efficiency under light and dark conditions. MIL-53 (Fe) MOF was synthesized using iron (III) and 1, 4-dicarboxylic acid under solvothermal conditions. The composite was synthesized similarly in the presence of TiO2 nanoparticles. The successful synthesis of MIL-53 (Fe) MOF and MOF/TiO composite was confirmed by powder X-ray diffraction and Fourier-transform infrared spectroscopy. By the Debye−Scherrer equation, 79.06 nm and 65.46 nm of crystallite size were obtained by the MOF and the MOF/TiO22 composite. Atomic absorption spectroscopy was used to determine the metal ion concentration before and after adsorption. The optimum conditions for the Pb(II) removal are as; 50 mg L-1, 25 mg L-1 initial Pb ion concentration, 10 mg, 12.5 mg of adsorbent dose (for 25 ml of 50 mg L-1 Pb (II)) and 90 min, 90 min contact time for both adsorbents at light and dark conditions respectively. The pH of the solution was kept at a neutral level to ensure the reusability of wastewater after the removal of pollutants. The adsorption isotherms of both adsorbents were well fitted with the Langmuir model indicating the monolayer adsorption. Thus, at pH 7, 396.35 mg g-1 and 786.16 mg g-1 of maximum Pb (II) adsorption capacity were obtained by the MOF and the MOF/TiO2 composite respectively. Thus, a significant improvement in the Pb (II) ion removal was observed with the composite compared to the MOF.  Keywords: Adsorption, Heavy metal, Isotherm, MIL-53 (Fe)
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