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载银纳米颗粒的磺化聚醚砜/聚醚砜静电纺纳米纤维膜用于去除重金属。

Ag nanoparticles immobilized sulfonated polyethersulfone/polyethersulfone electrospun nanofiber membrane for the removal of heavy metals.

机构信息

Shenzhen Institute of Advanced Technology, Chinese Academy of Sciences, Shenzhen, 518055, China.

University of Chinese Academy of Sciences, Beijing, 100049, China.

出版信息

Sci Rep. 2022 Apr 6;12(1):5814. doi: 10.1038/s41598-022-09802-9.

DOI:10.1038/s41598-022-09802-9
PMID:35388115
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC8986829/
Abstract

In this work, Eucommia ulmoides leaf extract (EUOLstabilized silver nanoparticles (EUOL@AgNPs) incorporated sulfonated polyether sulfone (SPES)/polyethersulfone (PES) electrospun nanofiber membranes (SP ENMs) were prepared by electrospinning, and they were studied for the removal of lead (Pb(II)) and cadmium (Cd(II)) ions from aqueous solutions. The SP ENMs with various EUOL@AgNPs loadings were characterized by X-ray diffraction (XRD), Fourier transform infrared (FTIR) spectroscope, thermo-gravimetric analysis (TGA), scanning electron microscopy (SEM), transmission electron microscopy (TEM), and contact angle (CA) measurements. The adsorption studies showed that the adsorption of Cd(II) and Pb(II) was rapid, achieved equilibrium within 40 min and 60 min, respectively and fitted with non-linear pseudo-second-order (PSO) kinetics model. For Cd(II) and Pb(II), the Freundlich model described the adsorption isotherm better than the Langmuir isotherm model. The maximum adsorption capacity for Cd(II) and Pb(II) was 625 and 370.37 mg g respectively at neutral pH. Coexisting anions of fluoride, chloride, and nitrate had a negligible influence on Cd(II) removal than the Pb(II). On the other hand, the presence of silicate and phosphate considerably affected Cd(II) and Pb(II) adsorption. The recyclability, regeneration, and reusability of the fabricated EUOL@AgNPs-SP ENMs were studied and they retained their high adsorption capacity up to five cycles. The DFT measurements revealed that SP-5 ENMs exhibited the highest adsorption selectivity for Cd(II) and the measured binding energies for Cd(II), Pb(II), are 219.35 and 206.26 kcal mol, respectively. The developed ENM adsorbent may find application for the removal of heavy metals from water.

摘要

在这项工作中,采用静电纺丝法制备了杜仲叶提取物(EUOL)稳定的银纳米粒子(EUOL@AgNPs)掺入磺化聚醚砜(SPES)/聚醚砜(PES)电纺纳米纤维膜(SP ENMs),并研究了它们对水溶液中铅(Pb(II))和镉(Cd(II))离子的去除。通过 X 射线衍射(XRD)、傅里叶变换红外(FTIR)光谱仪、热重分析(TGA)、扫描电子显微镜(SEM)、透射电子显微镜(TEM)和接触角(CA)测量对具有不同 EUOL@AgNPs 负载量的 SP ENMs 进行了表征。吸附研究表明,Cd(II)和 Pb(II)的吸附速度很快,分别在 40 min 和 60 min 内达到平衡,并符合非线性伪二阶(PSO)动力学模型。对于 Cd(II)和 Pb(II),Freundlich 模型比 Langmuir 等温线模型更好地描述了吸附等温线。在中性 pH 下,Cd(II)和 Pb(II)的最大吸附容量分别为 625 和 370.37 mg/g。与 Pb(II)相比,氟化物、氯化物和硝酸盐等共存阴离子对 Cd(II)的去除影响可以忽略不计。另一方面,硅酸盐和磷酸盐的存在对 Cd(II)和 Pb(II)的吸附有很大影响。研究了制备的 EUOL@AgNPs-SP ENMs 的可回收性、再生性和可重复使用性,它们在五个循环中保持了高吸附容量。DFT 测量结果表明,SP-5 ENMs 对 Cd(II)表现出最高的吸附选择性,Cd(II)的测量结合能为 219.35 和 206.26 kcal/mol。开发的 ENM 吸附剂可能在从水中去除重金属方面有应用。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/b20a07838479/41598_2022_9802_Fig9_HTML.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/4b3e36724d42/41598_2022_9802_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/739c918ad22a/41598_2022_9802_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/c0777355e1df/41598_2022_9802_Fig7_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/c952be5cd87c/41598_2022_9802_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/b20a07838479/41598_2022_9802_Fig9_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/df9bb3a377e7/41598_2022_9802_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/ff7bea24e59a/41598_2022_9802_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/1afbedbc71a8/41598_2022_9802_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/afb43b169277/41598_2022_9802_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/4b3e36724d42/41598_2022_9802_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/739c918ad22a/41598_2022_9802_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/c0777355e1df/41598_2022_9802_Fig7_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/c952be5cd87c/41598_2022_9802_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1dfa/8986829/b20a07838479/41598_2022_9802_Fig9_HTML.jpg

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