• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

偕胺肟基聚丙烯腈螯合纳米纤维的制备及其对金属离子的吸附应用

Preparation of Amidoxime Polyacrylonitrile Chelating Nanofibers and Their Application for Adsorption of Metal Ions.

作者信息

Huang Fenglin, Xu Yunfei, Liao Shiqin, Yang Dawei, Hsieh You-Lo, Wei Qufu

机构信息

Key Laboratory of Eco-Textiles, Ministry of Education, Jiangnan University, Wuxi 214122, China.

University of California Davis, Davis, CA 95616, USA.

出版信息

Materials (Basel). 2013 Mar 11;6(3):969-980. doi: 10.3390/ma6030969.

DOI:10.3390/ma6030969
PMID:28809351
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC5512958/
Abstract

Polyacrylonitrile (PAN) nanofibers were prepared by electrospinning and they were modified with hydroxylamine to synthesize amidoxime polyacrylonitrile (AOPAN) chelating nanofibers, which were applied to adsorb copper and iron ions. The conversion of the nitrile group in PAN was calculated by the gravimetric method. The structure and surface morphology of the AOPAN nanofiber were characterized by a Fourier transform infrared spectrometer (FT-IR) and a scanning electron microscope (SEM), respectively. The adsorption abilities of Cu and Fe ions onto the AOPAN nanofiber mats were evaluated. FT-IR spectra showed nitrile groups in the PAN were partly converted into amidoxime groups. SEM examination demonstrated that there were no serious cracks or sign of degradation on the surface of the PAN nanofibers after chemical modification. The adsorption capacities of both copper and iron ions onto the AOPAN nanofiber mats were higher than those into the raw PAN nanofiber mats. The adsorption data of Cu and Fe ions fitted particularly well with the Langmuir isotherm. The maximal adsorption capacities of Cu and Fe ions were 215.18 and 221.37 mg/g, respectively.

摘要

通过静电纺丝制备了聚丙烯腈(PAN)纳米纤维,并用羟胺对其进行改性以合成偕胺肟聚丙烯腈(AOPAN)螯合纳米纤维,将其用于吸附铜离子和铁离子。采用重量法计算PAN中腈基的转化率。分别用傅里叶变换红外光谱仪(FT-IR)和扫描电子显微镜(SEM)对AOPAN纳米纤维的结构和表面形貌进行了表征。评估了铜离子和铁离子在AOPAN纳米纤维毡上的吸附能力。FT-IR光谱表明PAN中的腈基部分转化为偕胺肟基团。SEM检查表明,化学改性后PAN纳米纤维表面没有严重的裂纹或降解迹象。铜离子和铁离子在AOPAN纳米纤维毡上的吸附容量均高于在原始PAN纳米纤维毡上的吸附容量。铜离子和铁离子的吸附数据与朗缪尔等温线拟合得特别好。铜离子和铁离子的最大吸附容量分别为215.18和221.37 mg/g。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/226e48abb6ce/materials-06-00969-g005a.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/3f2f7b491bf1/materials-06-00969-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/1a5bc406e839/materials-06-00969-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/47b6b4f23e54/materials-06-00969-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/c832f28bd3c3/materials-06-00969-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/39b2c40ce9a4/materials-06-00969-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/226e48abb6ce/materials-06-00969-g005a.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/3f2f7b491bf1/materials-06-00969-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/1a5bc406e839/materials-06-00969-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/47b6b4f23e54/materials-06-00969-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/c832f28bd3c3/materials-06-00969-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/39b2c40ce9a4/materials-06-00969-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2305/5512958/226e48abb6ce/materials-06-00969-g005a.jpg

相似文献

1
Preparation of Amidoxime Polyacrylonitrile Chelating Nanofibers and Their Application for Adsorption of Metal Ions.偕胺肟基聚丙烯腈螯合纳米纤维的制备及其对金属离子的吸附应用
Materials (Basel). 2013 Mar 11;6(3):969-980. doi: 10.3390/ma6030969.
2
Preparation of aminated-polyacrylonitrile nanofiber membranes for the adsorption of metal ions: comparison with microfibers.用于吸附金属离子的氨基化聚丙烯腈纳米纤维膜的制备:与微纤维的比较。
J Hazard Mater. 2011 Feb 15;186(1):182-9. doi: 10.1016/j.jhazmat.2010.10.121. Epub 2010 Nov 12.
3
Electrospun AOPAN/RC blend nanofiber membrane for efficient removal of heavy metal ions from water.静电纺丝 AOPAN/RC 共混纳米纤维膜用于高效去除水中重金属离子。
J Hazard Mater. 2018 Feb 15;344:819-828. doi: 10.1016/j.jhazmat.2017.11.035. Epub 2017 Nov 21.
4
Starch-graft-polyacrylonitrile nanofibers by electrospinning.电纺丝法制备淀粉接枝聚丙烯腈纳米纤维。
Int J Biol Macromol. 2018 Dec;120(Pt B):2552-2559. doi: 10.1016/j.ijbiomac.2018.09.031. Epub 2018 Sep 6.
5
Preparation and adsorption behavior of aminated electrospun polyacrylonitrile nanofiber mats for heavy metal ion removal.用于重金属离子去除的氨基化静电纺聚丙烯腈纳米纤维垫的制备及其吸附行为。
ACS Appl Mater Interfaces. 2010 Dec;2(12):3619-27. doi: 10.1021/am1008024. Epub 2010 Nov 30.
6
Adsorption of antimonite and antimonate from aqueous solution using modified polyacrylonitrile with an ultrahigh percentage of amidoxime groups.采用超高偕胺肟基团含量的改性聚丙烯腈从水溶液中吸附亚锑酸盐和锑酸盐。
J Hazard Mater. 2020 Apr 15;388:121997. doi: 10.1016/j.jhazmat.2019.121997. Epub 2019 Dec 30.
7
Thermodynamic and kinetic analysis of the response surface method for phenol removal from aqueous solution using graphene oxide-polyacrylonitrile nanofiber mats.氧化石墨烯-聚丙烯腈纳米纤维毡用于从水溶液中去除苯酚的响应面法的热力学和动力学分析
Sci Rep. 2024 Feb 12;14(1):3531. doi: 10.1038/s41598-024-53572-5.
8
Adsorption performance of Cd(II), Cr(III), Cu(II), Ni(II), Pb(II) and Zn(II) by aminated solution-blown polyacrylonitrile micro/nanofibers.胺化溶液吹塑聚丙烯腈微/纳米纤维对Cd(II)、Cr(III)、Cu(II)、Ni(II)、Pb(II)和Zn(II)的吸附性能
Water Sci Technol. 2018 May;2017(2):378-389. doi: 10.2166/wst.2018.161.
9
Comparative Removal of Lead and Nickel Ions onto Nanofibrous Sheet of Activated Polyacrylonitrile in Batch Adsorption and Application of Conventional Kinetic and Isotherm Models.间歇吸附中活性聚丙烯腈纳米纤维片对铅离子和镍离子的去除比较及传统动力学和等温线模型的应用
Membranes (Basel). 2020 Dec 23;11(1):10. doi: 10.3390/membranes11010010.
10
Electrospinning of calixarene-functionalized polyacrylonitrile nanofiber membranes and application as an adsorbent and catalyst support.杯芳烃功能化聚丙烯腈纳米纤维膜的静电纺丝及其作为吸附剂和催化剂载体的应用。
Langmuir. 2013 Sep 24;29(38):11858-67. doi: 10.1021/la4017799. Epub 2013 Sep 11.

引用本文的文献

1
Solution-processable polymer membranes with hydrophilic subnanometre pores for sustainable lithium extraction.用于可持续锂提取的具有亲水性亚纳米孔的溶液可加工聚合物膜。
Nat Water. 2025;3(3):319-333. doi: 10.1038/s44221-025-00398-8. Epub 2025 Mar 12.
2
The Potential of Electrospun Membranes in the Treatment of Textile Wastewater: A Review.静电纺丝膜在纺织废水处理中的潜力:综述
Polymers (Basel). 2024 Mar 13;16(6):801. doi: 10.3390/polym16060801.
3
Advances of polyolefins from fiber to nanofiber: fabrication and recent applications.

本文引用的文献

1
Preparation of aminated-polyacrylonitrile nanofiber membranes for the adsorption of metal ions: comparison with microfibers.用于吸附金属离子的氨基化聚丙烯腈纳米纤维膜的制备:与微纤维的比较。
J Hazard Mater. 2011 Feb 15;186(1):182-9. doi: 10.1016/j.jhazmat.2010.10.121. Epub 2010 Nov 12.
2
Filtration by a novel nanofiber membrane and alumina adsorption to remove copper(II) from groundwater.通过新型纳米纤维膜过滤和氧化铝吸附去除地下水中的铜(II)。
J Hazard Mater. 2008 May 1;153(1-2):860-6. doi: 10.1016/j.jhazmat.2007.09.035. Epub 2007 Sep 14.
3
Hybrid biosorbent: An innovative matrix to enhance the biosorption of Cd(II) from aqueous solution.
聚烯烃从纤维到纳米纤维的进展:制备方法与近期应用
Discov Nano. 2024 Feb 6;19(1):24. doi: 10.1186/s11671-023-03945-y.
4
A comprehensive review on triple R eco-management strategies to reduce, reuse and recycle of hazardous cigarette butts.关于减少、再利用和回收有害烟头的三重R生态管理策略的综合综述。
Heliyon. 2023 May 27;9(6):e16642. doi: 10.1016/j.heliyon.2023.e16642. eCollection 2023 Jun.
5
Recent advances and remaining barriers to the development of electrospun nanofiber and nanofiber composites for point-of-use and point-of-entry water treatment systems.用于现场和入口处水处理系统的电纺纳米纤维及纳米纤维复合材料开发的最新进展与尚存障碍
J Hazard Mater Adv. 2022 Nov;8. doi: 10.1016/j.hazadv.2022.100204. Epub 2022 Nov 19.
6
Reversible flowering of CuO nanoclusters via conversion reaction for dual-ion Li metal batteries.用于双离子锂金属电池的通过转化反应实现的CuO纳米团簇可逆开花
Nano Converg. 2023 Jan 13;10(1):4. doi: 10.1186/s40580-022-00353-3.
7
A Review on Polyacrylonitrile as an Effective and Economic Constituent of Adsorbents for Wastewater Treatment.聚丙烯腈作为一种有效且经济的吸附剂成分在废水处理中的应用综述。
Molecules. 2022 Dec 8;27(24):8689. doi: 10.3390/molecules27248689.
8
U(VI) binding onto electrospun polymers functionalized with phosphonate surfactants.铀(VI)与用膦酸盐表面活性剂功能化的电纺聚合物的结合。
J Environ Chem Eng. 2022 Oct;10(5). doi: 10.1016/j.jece.2022.108448. Epub 2022 Aug 17.
9
Recent Progress in Electrospun Polyacrylonitrile Nanofiber-Based Wound Dressing.基于静电纺聚丙烯腈纳米纤维的伤口敷料的最新进展
Polymers (Basel). 2022 Aug 11;14(16):3266. doi: 10.3390/polym14163266.
10
Nanocomposite functionalized membranes based on silica nanoparticles cross-linked to electrospun nanofibrous support for arsenic(v) adsorption from contaminated underground water.基于与电纺纳米纤维载体交联的二氧化硅纳米颗粒的纳米复合功能化膜,用于从受污染的地下水中吸附砷(Ⅴ)。
RSC Adv. 2019 Mar 12;9(15):8280-8289. doi: 10.1039/c8ra09866b.
混合生物吸附剂:一种用于增强从水溶液中生物吸附Cd(II)的创新基质。
J Hazard Mater. 2007 Sep 5;148(1-2):47-55. doi: 10.1016/j.jhazmat.2007.02.009. Epub 2007 Feb 11.
4
Electrospinning of polymeric nanofibers for tissue engineering applications: a review.用于组织工程应用的聚合物纳米纤维静电纺丝:综述
Tissue Eng. 2006 May;12(5):1197-211. doi: 10.1089/ten.2006.12.1197.
5
Simultaneous heavy metal removal mechanism by dead macrophytes.死亡大型植物同步去除重金属的机制
Chemosphere. 2006 Jan;62(2):247-54. doi: 10.1016/j.chemosphere.2005.05.010. Epub 2005 Jun 28.
6
Adsorption of zinc on bed sediment of River Hindon: adsorption models and kinetics.锌在欣登河河床上的吸附:吸附模型与动力学
J Hazard Mater. 2004 Oct 18;114(1-3):231-9. doi: 10.1016/j.jhazmat.2004.09.001.
7
Kinetics and equilibrium adsorption study of lead(II) onto activated carbon prepared from coconut shell.椰壳制备的活性炭对铅(II)的吸附动力学及平衡吸附研究
J Colloid Interface Sci. 2004 Nov 15;279(2):307-13. doi: 10.1016/j.jcis.2004.06.042.
8
Release of tetracycline hydrochloride from electrospun poly(ethylene-co-vinylacetate), poly(lactic acid), and a blend.盐酸四环素从电纺聚(乙烯 - 醋酸乙烯酯)、聚乳酸及其共混物中的释放。
J Control Release. 2002 May 17;81(1-2):57-64. doi: 10.1016/s0168-3659(02)00041-x.