大豆皮过氧化物酶提取后的回收及其作为金属离子和染料吸附剂的应用

A. Ivanovska, B. Dojčinović, Jelena M. Lađarević, Leposava Pavun, D. Mijin, M. Kostić, M. Svetozarević
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引用次数: 0

摘要

本研究旨在通过利用大豆皮作为金属离子(Cd2+和Cu2+)和染料(活性黄39 (RY 39)和酸性蓝225 (AB 225))的吸附剂来延长大豆皮的使用寿命。ATR-FTIR光谱,FE-SEM显微镜和zeta电位测量用于吸附剂的表征。考察了溶液pH、过氧化物酶萃取量、吸附剂粒径、接触时间、污染物初始浓度、温度等因素对大豆皮吸附电位的影响。在过氧化物酶提取前,大豆皮对Cd2+的去除率为72%,Cu2+的去除率为71% (pH = 5.00), RY 39的去除率为81%,AB 225的去除率为73% (pH = 3.00)。在进一步的实验中,使用不含过氧化物酶的大豆皮有以下几个原因:(1)由于观察到它们具有更高的金属离子去除率,(2)为了降低过氧化物酶(通常用于废水脱色)提取后的废物处理成本,(3)因为不含过氧化物酶的大豆皮具有明显低于含过氧化物酶的大豆皮的二次污染。当吸附剂粒径较小(710 ~ 1000 μm)时,Cd2+和Cu2+的去除率略有提高,而吸附剂粒径对染料去除率没有影响。接触30 min后,RY 39和AB 225的去除率分别为92%和88%,相同接触时间后,Cd2+和Cu2+的去除率分别为80%和69%。所有被测污染物的吸附遵循伪二级反应,经过快速吸附、颗粒内扩散和最终平衡阶段。Langmuir模型对Cd2+、Cu2+、RY 39和AB 225的最大吸附量分别为21.10、20.54、16.54和17.23 mg/g。计算的热力学参数表明,所有污染物的吸附都是自发的,具有吸热特性。此外,制备了不同的二元混合物,并对其进行了竞争吸附,结果表明大豆壳是ab225和Cu2+混合物的最有效吸附剂。本研究结果有助于过氧化物酶提取后的大豆皮的回收,并将其纳入循环经济的概念。
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Recovering the Soybean Hulls after Peroxidase Extraction and Their Application as Adsorbent for Metal Ions and Dyes
This study is aimed at extending the soybean hulls’ lifetime by their utilization as an adsorbent for metal ions (Cd2+ and Cu2+) and dyes (Reactive Yellow 39 (RY 39) and Acid Blue 225 (AB 225)). ATR-FTIR spectroscopy, FE-SEM microscopy, and zeta potential measurements were used for adsorbent characterization. The effect of the solution’s pH, peroxidase extraction, adsorbent particle size, contact time, the pollutant’s initial concentration, and temperature on the soybean hulls’ adsorption potential was studied. Before peroxidase extraction, soybean hulls were capable of removing 72% Cd2+, 71% Cu2+ (at a pH of 5.00) or 81% RY 39, and 73% AB 225 (at a pH of 3.00). For further experiments, soybean hulls without peroxidase were used for several reasons: (1) due to their observed higher metal ion removal, (2) in order to reduce the waste disposal cost after the peroxidase (usually used for wastewater decolorization) extraction, and (3) since the soybean hulls without peroxidase possessed significantly lower secondary pollution than those with peroxidase. Cd2+ and Cu2+ removal was slightly increased when the smaller adsorbent fraction (710-1000 μm) was used, while the adsorbent particle size did not have an impact on dye removal. After 30 min of contact time, 92% and 88% of RY 39 and AB 225 were removed, respectively, while after the same contact time, 80% and 69% of Cd2+ and Cu2+ were removed, respectively. Adsorption of all tested pollutants follows a pseudo-second-order reaction through the fast adsorption, intraparticle diffusion, and final equilibrium stage. The maximal adsorption capacities determined by the Langmuir model were 21.10, 20.54, 16.54, and 17.23 mg/g for Cd2+, Cu2+, RY 39, and AB 225, respectively. Calculated thermodynamic parameters suggested that the adsorption of all pollutants is spontaneous and of endothermic character. Moreover, different binary mixtures were prepared, and the competitive adsorptions revealed that the soybean hulls are the most efficient adsorbent for the mixture of AB 225 and Cu2+. The findings of this study contribute to the soybean hulls’ recovery after the peroxidase extraction and bring them into the circular economy concept.
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