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深入了解 Pb(II)与水果废料生物吸附剂之间的相互作用。

New insights into the interactions between Pb(II) and fruit waste biosorbent.

机构信息

Department of Physics, Chemistry and Pharmacy, University of Southern Denmark, 5230, Odense M, Denmark.

Key Laboratory of Protected Horticulture Engineering in Northwest, Ministry of Agriculture, College of Horticulture, Northwest A&F University, Yangling, Shaanxi, 712100, China.

出版信息

Chemosphere. 2022 Sep;303(Pt 1):135048. doi: 10.1016/j.chemosphere.2022.135048. Epub 2022 May 22.

DOI:10.1016/j.chemosphere.2022.135048
PMID:35613637
Abstract

Fruit waste is a sustainable biosorbent for heavy metal removal from wastewater. Elucidation of adsorption mechanism is imperative for the process control and development of effective adsorbents. In this study, watermelon rind (WR) exhibited selective and efficient Pb(II) adsorption with a maximum uptake of 230.5 mg/g at pH 5.0. The WR-packed bed column showed high Pb(II) uptake and robust durability over 10 adsorption-desorption cycles with long breakthrough time of 8-13 h (89-144 bed volume), and 95% of sequestered Pb(II) was rapidly desorbed in 1-2 h by 0.05 M HCl. Spectroscopic characterization by FTIR and XPS identified hydroxyl, carboxyl, amine, and ether groups as the binding sites for Pb(II) via the binding force of complexation. Physicochemical analysis showed that ion exchange with Mg and Ca accounted for 19% of Pb(II) adsorption by WR; electrostatic attraction and microprecipitation jointly contributed. Quantum chemistry simulation verified the interactions between Pb(II) and binding sites and revealed carboxyl was the preferential functional group. The findings corroborate the applicability of WR in scale-up Pb(II) removal/recovery from wastewater and elaborate the mechanisms of Pb(II) adsorption by the WR biosorbent. This also provides insights into the behavior of heavy metals in other liquid/solid interfaces.

摘要

果皮是一种可持续的生物吸附剂,可用于从废水中去除重金属。阐明吸附机制对于过程控制和有效吸附剂的开发至关重要。在这项研究中,西瓜皮(WR)在 pH 值为 5.0 时对 Pb(II)表现出选择性和高效的吸附,最大吸附量为 230.5 mg/g。WR 填充床柱在 10 次吸附-解吸循环中表现出高的 Pb(II)摄取量和强大的耐用性,穿透时间长达 8-13 小时(89-144 床体积),并且 95%被螯合的 Pb(II)可在 1-2 小时内用 0.05 M HCl 快速解吸。通过 FTIR 和 XPS 的光谱特征分析,确定了羟基、羧基、胺和醚基是 WR 与 Pb(II)结合的结合位点,结合力为络合。物理化学分析表明,WR 对 Pb(II)的吸附中,离子交换与 Mg 和 Ca 占 19%;静电吸引和微沉淀共同作用。量子化学模拟验证了 Pb(II)与结合位点之间的相互作用,并表明羧基是优先的官能团。这些发现证实了 WR 在从废水中规模化去除/回收 Pb(II)方面的适用性,并详细阐述了 WR 生物吸附剂对 Pb(II)吸附的机制。这也为深入了解重金属在其他液/固界面上的行为提供了参考。

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