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采用以废铸造尘为磁性材料的聚乙烯亚胺交联海藻酸钠珠粒从水溶液中去除甲基红。

Removal of Methyl Red from Aqueous Solution Using Polyethyleneimine Crosslinked Alginate Beads with Waste Foundry Dust as a Magnetic Material.

机构信息

Department of Energy and Resource Engineering, Chosun University, Gwangju 61452, Korea.

Green-Bio Research Facility Center, Seoul National University, Pyeongchang-gun 25354, Korea.

出版信息

Int J Environ Res Public Health. 2022 Jul 25;19(15):9030. doi: 10.3390/ijerph19159030.

DOI:10.3390/ijerph19159030
PMID:35897402
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC9330805/
Abstract

In this study, a cost-effective adsorbent based on sodium alginate (SA) with waste foundry dust (WFD) was fabricated for the removal of methyl red (MR) from aqueous media. However, the utilization of WFD/SA beads to remove anionic dyes (such as MR) from effluents has limitations associated with their functional groups. To improve the adsorption performance, WFD/SA-polyethyleneimine (PEI) beads were formed via PEI crosslinking onto WFD/SA beads, which could be attributed to the formation of amide bonds from the carboxyl and amino groups due to the change of N-H bonds in the reaction. The Fourier transform infrared (FTIR) and X-ray photoelectron spectroscopy (XPS) results indicated that PEI was crosslinked on the WFD/SA via a chemical reaction. In the FTIR spectra of WFD/SA-PEI, peaks of the -COO (asymmetric) stretching vibration shifted to 1598 and 1395 cm, which could be attributed to the hydrogen-bonding effect of the N-H groups in PEI. In the N1s spectrum, three deconvoluted peaks were assigned to N in -N= (398.2 eV), -NH/-NH (399.6 eV), and NO (405.2 eV). WFD/SA-PEI beads were assessed and optimized for aqueous MR adsorption. The WFD/SA-PEI beads showed a high removal efficiency for MR (89.1%) at an initial concentration of 1000 mg/L, and presented a maximum MR adsorption capacity of 672.7 mg/g MR. The adsorption process showed a good fit with the pseudo-second-order kinetic model and the Langmuir adsorption isotherm model. The amino and hydroxyl groups in the WFD/SA-PEI beads facilitate strong hydrogen bonding and electrostatic interactions. Moreover, these WFD/SA-PEI beads were easily recovered after the adsorption process.

摘要

在这项研究中,制备了一种基于海藻酸钠(SA)的具有成本效益的吸附剂,该吸附剂利用废铸造砂(WFD),用于从水介质中去除甲基红(MR)。然而,利用 WFD/SA 珠粒从废水中去除阴离子染料(如 MR)存在与它们的官能团相关的限制。为了提高吸附性能,通过 PEI 交联到 WFD/SA 珠粒上形成 WFD/SA-聚乙烯亚胺(PEI)珠粒,这可以归因于由于反应中 N-H 键的变化,羧基和氨基之间形成酰胺键。傅里叶变换红外(FTIR)和 X 射线光电子能谱(XPS)结果表明,PEI 通过化学反应交联在 WFD/SA 上。在 WFD/SA-PEI 的 FTIR 光谱中,-COO(不对称)伸缩振动峰移至 1598 和 1395 cm,这可以归因于 PEI 中 N-H 基团的氢键效应。在 N1s 光谱中,三个解卷积峰被分配给-N=(398.2 eV),-NH/-NH(399.6 eV)和 NO(405.2 eV)中的 N。评估并优化了 WFD/SA-PEI 珠粒用于水溶液中 MR 的吸附。WFD/SA-PEI 珠粒在初始浓度为 1000 mg/L 时对 MR 具有高去除效率(89.1%),并表现出 672.7 mg/g MR 的最大 MR 吸附容量。吸附过程很好地符合准二级动力学模型和 Langmuir 吸附等温线模型。WFD/SA-PEI 珠粒中的氨基和羟基促进了强氢键和静电相互作用。此外,这些 WFD/SA-PEI 珠粒在吸附过程后很容易回收。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/224418a83c67/ijerph-19-09030-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/ef0cb92ce274/ijerph-19-09030-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/f449f4c4f37c/ijerph-19-09030-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/3e23a0262261/ijerph-19-09030-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/3fe9ff39b07c/ijerph-19-09030-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/8b4d77d0422d/ijerph-19-09030-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/3d17194c3377/ijerph-19-09030-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/5a288cc7987c/ijerph-19-09030-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/875c166fe549/ijerph-19-09030-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/5b170863f7bf/ijerph-19-09030-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/20d339dc151c/ijerph-19-09030-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/224418a83c67/ijerph-19-09030-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/ef0cb92ce274/ijerph-19-09030-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/f449f4c4f37c/ijerph-19-09030-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/3e23a0262261/ijerph-19-09030-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/3fe9ff39b07c/ijerph-19-09030-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/8b4d77d0422d/ijerph-19-09030-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/3d17194c3377/ijerph-19-09030-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/5a288cc7987c/ijerph-19-09030-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/875c166fe549/ijerph-19-09030-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/5b170863f7bf/ijerph-19-09030-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/20d339dc151c/ijerph-19-09030-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f97b/9330805/224418a83c67/ijerph-19-09030-g011.jpg

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