• 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

催化湿式空气氧化法处理苯酚:负载于γ-氧化铝、二氧化铈以及γ-氧化铝-二氧化铈上的铜和镍的对比研究

Treatment of phenol by catalytic wet air oxidation: a comparative study of copper and nickel supported on γ-alumina, ceria and γ-alumina-ceria.

作者信息

Guerra-Que Zenaida, Pérez-Vidal Hermicenda, Torres-Torres G, Arévalo-Pérez Juan Carlos, Silahua Pavón Adib Abiu, Cervantes-Uribe Adrian, Espinosa de Los Monteros A, Lunagómez-Rocha Ma Antonia

机构信息

Laboratory of Catalytic Nanomaterials Applied to the Development of Energy Sources and Environmental Remediation, Applied Science and Technology Research Center of Tabasco (CICTAT), Juarez Autonomous University of Tabasco, DACB Road Km. 1 Cunduacan-Jalpa de Mendez Cunduacan Tabasco C.P. 86690 Mexico

出版信息

RSC Adv. 2019 Mar 13;9(15):8463-8479. doi: 10.1039/c9ra00509a. eCollection 2019 Mar 12.

DOI:10.1039/c9ra00509a
PMID:35547604
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC9087632/
Abstract

Cu, Ni, CuO and NiO catalysts, prepared by wet impregnation with urea and supported on γ-AlO, CeO, and AlO-CeO, were evaluated for Catalytic Wet Air Oxidation (CWAO) of phenol in a batch reactor under a milder condition (120 °C and 10 bar O). The synthesized samples, at their calcined and/or their reduced form, were characterized by XRD, H-TPR, N adsorption-desorption, SEM-EDS and DR-UV-Vis to explain the differences observed in their catalytic activity towards the studied reaction. The influence of the support on the efficiency of CWAO of phenol at 120 °C and 10 bar of pure oxygen has been examined and compared over nickel and copper species. The SEM-EDS results reveal that the spherical crystalline Cu and Ni were successfully deposited on the surface of γ-AlO, CeO, AlO-CeO within 16-90 nm and that they were highly homogeneously dispersed. It was found that catalysts prepared from impregnation solutions of Cu(NO)·3HO and Ni(NO)·6HO with urea addition had different textural characteristics and degrees of dispersion of Cu and Ni species. The urea addition in the traditional wet impregnation method was essential to improve the reducibility and degree of dispersion in Ni, and to a lesser extent, in Cu. According to the characterization analysis of H-TPR and UV-VIS RD a structure-activity relationship can be determined. The chemical oxygen demand (COD) and GC analyses confirmed the effect of calcined and reduced species for Cu and Ni applied to the catalytic oxidation of phenol, showing their significant impact in the final performance of the catalyst.

摘要

通过尿素湿浸渍法制备并负载于γ-Al₂O₃、CeO₂以及Al₂O₃-CeO₂上的铜、镍、氧化铜和氧化镍催化剂,在间歇式反应器中于较温和条件(120℃和10 bar O₂)下对苯酚的催化湿式空气氧化(CWAO)进行了评估。对合成后的样品在其煅烧态和/或还原态下进行了X射线衍射(XRD)、氢气程序升温还原(H-TPR)、氮气吸附-脱附、扫描电子显微镜-能谱分析(SEM-EDS)以及漫反射紫外可见光谱(DR-UV-Vis)表征,以解释观察到的它们对所研究反应的催化活性差异。研究并比较了载体对120℃和10 bar纯氧条件下苯酚CWAO效率的影响,涉及镍和铜物种。SEM-EDS结果表明,球形结晶的铜和镍成功沉积在γ-Al₂O₃、CeO₂、Al₂O₃-CeO₂表面,粒径在16 - 90 nm之间,且高度均匀分散。发现由添加尿素的Cu(NO₃)₂·3H₂O和Ni(NO₃)₂·6H₂O浸渍溶液制备的催化剂具有不同的织构特征以及铜和镍物种的分散程度。在传统湿浸渍法中添加尿素对于提高镍的还原度和分散程度至关重要,对铜的影响程度较小。根据H-TPR和UV-VIS RD的表征分析,可以确定结构-活性关系。化学需氧量(COD)和气相色谱(GC)分析证实了煅烧态和还原态的铜和镍物种对苯酚催化氧化的作用,显示出它们对催化剂最终性能的显著影响。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/9cf4792b9ed9/c9ra00509a-f16.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/408c6eac5eed/c9ra00509a-f1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/948d3cc9eb32/c9ra00509a-f2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/bd6f2f008f9d/c9ra00509a-f3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/5bb959c72306/c9ra00509a-f4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/8e48ace12ba4/c9ra00509a-f5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/270c5a1b6fc6/c9ra00509a-f6.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/2aae291b1c64/c9ra00509a-f7.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/c114a2953fa8/c9ra00509a-f8.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/28d7f4c84bf3/c9ra00509a-f9.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/0e89e31e3214/c9ra00509a-f10.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/facaacf5d49d/c9ra00509a-f11.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/53768f3d898c/c9ra00509a-f12.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/ee9ea9a86a82/c9ra00509a-f13.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/1d5a71de4a85/c9ra00509a-f14.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/7e650a341273/c9ra00509a-f15.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/9cf4792b9ed9/c9ra00509a-f16.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/408c6eac5eed/c9ra00509a-f1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/948d3cc9eb32/c9ra00509a-f2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/bd6f2f008f9d/c9ra00509a-f3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/5bb959c72306/c9ra00509a-f4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/8e48ace12ba4/c9ra00509a-f5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/270c5a1b6fc6/c9ra00509a-f6.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/2aae291b1c64/c9ra00509a-f7.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/c114a2953fa8/c9ra00509a-f8.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/28d7f4c84bf3/c9ra00509a-f9.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/0e89e31e3214/c9ra00509a-f10.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/facaacf5d49d/c9ra00509a-f11.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/53768f3d898c/c9ra00509a-f12.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/ee9ea9a86a82/c9ra00509a-f13.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/1d5a71de4a85/c9ra00509a-f14.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/7e650a341273/c9ra00509a-f15.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f4b7/9087632/9cf4792b9ed9/c9ra00509a-f16.jpg

相似文献

1
Treatment of phenol by catalytic wet air oxidation: a comparative study of copper and nickel supported on γ-alumina, ceria and γ-alumina-ceria.催化湿式空气氧化法处理苯酚:负载于γ-氧化铝、二氧化铈以及γ-氧化铝-二氧化铈上的铜和镍的对比研究
RSC Adv. 2019 Mar 13;9(15):8463-8479. doi: 10.1039/c9ra00509a. eCollection 2019 Mar 12.
2
Bimetallic M-Cu (M = Ag, Au, Ni) Nanoparticles Supported on γAlO-CeO Synthesized by a Redox Method Applied in Wet Oxidation of Phenol in Aqueous Solution and Petroleum Refinery Wastewater.通过氧化还原法合成的负载在γAlO-CeO上的双金属M-Cu(M = Ag、Au、Ni)纳米颗粒在苯酚水溶液和石油炼制废水的湿式氧化中的应用
Nanomaterials (Basel). 2021 Sep 30;11(10):2570. doi: 10.3390/nano11102570.
3
Insight into catalytic performance and reaction mechanism for toluene total oxidation over Cu-Ce supported catalyst.深入了解负载型 Cu-Ce 催化剂上甲苯完全氧化的催化性能和反应机理。
J Environ Sci (China). 2025 Mar;149:476-487. doi: 10.1016/j.jes.2024.01.001. Epub 2024 Jan 18.
4
Catalytic activity of Cu/η-AlO catalysts prepared from aluminum scraps in the NH-SCO and in the NH-SCR of NO.由废铝制备的 Cu/η-AlO 催化剂在 NH-SCO 和 NH-SCR 中对 NO 的催化活性。
Environ Sci Pollut Res Int. 2022 Feb;29(6):9053-9064. doi: 10.1007/s11356-021-16206-1. Epub 2021 Sep 8.
5
Degradation of phenol via wet-air oxidation over CuO/CeO2-ZrO2 nanocatalyst synthesized employing ultrasound energy: physicochemical characterization and catalytic performance.采用超声能量合成的 CuO/CeO2-ZrO2 纳米催化剂用于湿空气氧化法降解苯酚:物理化学特性表征和催化性能。
Environ Technol. 2014 May-Jun;35(9-12):1140-9. doi: 10.1080/09593330.2013.863952.
6
Enhancement of Ni-NiO-CeO Interaction on Ni-CeO/AlO-MgO Catalyst by Ammonia Vapor Diffusion Impregnation for CO Reforming of CH.通过氨蒸气扩散浸渍增强Ni-CeO/AlO-MgO催化剂上Ni-NiO-CeO的相互作用用于CH的CO重整
Molecules. 2024 Jun 12;29(12):2803. doi: 10.3390/molecules29122803.
7
Hydrogen Production by Ethanol Reforming on Supported Ni-Cu Catalysts.负载型镍铜催化剂上乙醇重整制氢
ACS Omega. 2022 Jan 31;7(5):4577-4584. doi: 10.1021/acsomega.1c06579. eCollection 2022 Feb 8.
8
Catalytic wet air oxidation of phenol over CeO2-TiO2 catalyst in the batch reactor and the packed-bed reactor.在间歇式反应器和填充床反应器中,CeO₂-TiO₂ 催化剂上苯酚的催化湿式空气氧化。
J Hazard Mater. 2008 May 30;153(3):1248-53. doi: 10.1016/j.jhazmat.2007.09.084. Epub 2007 Sep 29.
9
Partial Oxidation of Methane to Syngas Over Nickel-Based Catalysts: Influence of Support Type, Addition of Rhodium, and Preparation Method.镍基催化剂上甲烷部分氧化制合成气:载体类型、铑的添加及制备方法的影响
Front Chem. 2019 Mar 13;7:104. doi: 10.3389/fchem.2019.00104. eCollection 2019.
10
Kinetics study on catalytic wet air oxidation of phenol by several metal oxide catalysts.几种金属氧化物催化剂催化湿式空气氧化苯酚的动力学研究
J Environ Sci (China). 2004;16(4):556-8.

引用本文的文献

1
Fabrication of a Ceramic Foam Catalyst Using Polymer Foam Scrap via the Replica Technique for Dry Reforming.通过复制技术利用聚合物泡沫废料制备用于干重整的陶瓷泡沫催化剂。
ACS Omega. 2022 Jan 27;7(5):4202-4213. doi: 10.1021/acsomega.1c05841. eCollection 2022 Feb 8.
2
Bimetallic M-Cu (M = Ag, Au, Ni) Nanoparticles Supported on γAlO-CeO Synthesized by a Redox Method Applied in Wet Oxidation of Phenol in Aqueous Solution and Petroleum Refinery Wastewater.通过氧化还原法合成的负载在γAlO-CeO上的双金属M-Cu(M = Ag、Au、Ni)纳米颗粒在苯酚水溶液和石油炼制废水的湿式氧化中的应用
Nanomaterials (Basel). 2021 Sep 30;11(10):2570. doi: 10.3390/nano11102570.
3

本文引用的文献

1
Generation and characterization of DOM in wastewater treatment processes.在废水处理过程中 DOM 的产生和特性。
Chemosphere. 2018 Jun;201:96-109. doi: 10.1016/j.chemosphere.2018.02.124. Epub 2018 Feb 27.
2
Degradation process analysis of the azo dyes by catalytic wet air oxidation with catalyst CuO/γ-Al2O3.催化湿式氧化法中氧化铜/γ-氧化铝催化剂对偶氮染料的降解过程分析。
Chemosphere. 2013 Jan;90(2):143-9. doi: 10.1016/j.chemosphere.2012.06.018. Epub 2012 Jul 13.
3
Synthesis and physicochemical characterizations of nanostructured Pt/Al2O3-CeO2 catalysts for total oxidation of VOCs.
Chemical and Structural Changes by Gold Addition Using Recharge Method in NiW/AlO-CeO-TiO Nanomaterials.
采用充电法在NiW/AlO-CeO-TiO纳米材料中添加金引起的化学和结构变化
Materials (Basel). 2021 Sep 22;14(19):5470. doi: 10.3390/ma14195470.
4
Ti-Doped SBA-15 Catalysts Used in Phenol Oxidation Reactions.用于苯酚氧化反应的钛掺杂SBA-15催化剂。
ACS Omega. 2019 Dec 30;5(1):791-798. doi: 10.1021/acsomega.9b03530. eCollection 2020 Jan 14.
5
Effect of the CuAlO and CuAlO Phases in Catalytic Wet Air Oxidation of ETBE and TAME using CuO/γ-AlO catalysts.CuO/γ-Al₂O₃催化剂中CuAlO和CuAlO相在催化湿式空气氧化乙基叔丁基醚和甲基叔戊基醚中的作用。
ChemistryOpen. 2019 Aug 28;8(8):1143-1150. doi: 10.1002/open.201900080. eCollection 2019 Aug.
用于挥发性有机化合物完全氧化的纳米结构 Pt/Al2O3-CeO2 催化剂的合成及物理化学特性。
J Hazard Mater. 2011 Feb 28;186(2-3):1445-54. doi: 10.1016/j.jhazmat.2010.12.034. Epub 2010 Dec 14.
4
Ruthenium versus platinum on cerium materials in wet air oxidation of acetic acid.铱与铂在乙酸在湿空气氧化铈材料中的比较。
J Hazard Mater. 2010 Sep 15;181(1-3):633-9. doi: 10.1016/j.jhazmat.2010.05.059.
5
Catalytic wet air oxidation of phenol over CeO2-TiO2 catalyst in the batch reactor and the packed-bed reactor.在间歇式反应器和填充床反应器中,CeO₂-TiO₂ 催化剂上苯酚的催化湿式空气氧化。
J Hazard Mater. 2008 May 30;153(3):1248-53. doi: 10.1016/j.jhazmat.2007.09.084. Epub 2007 Sep 29.