• 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

新型光催化剂Bi₂GaSbO₇和Bi₂InSbO₇在可见光照射下的结构、光催化性能表征及增强的光催化活性

The Structural, Photocatalytic Property Characterization and Enhanced Photocatalytic Activities of Novel Photocatalysts Bi₂GaSbO₇ and Bi₂InSbO₇ during Visible Light Irradiation.

作者信息

Luan Jingfei, Shen Yue, Li Yanyan, Paz Yaron

机构信息

State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Nanjing 210093, China.

Department of Chemical Engineering, Technion-Israel Institute of Technology, Haifa 32000, Israel.

出版信息

Materials (Basel). 2016 Sep 27;9(10):801. doi: 10.3390/ma9100801.

DOI:10.3390/ma9100801
PMID:28773922
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC5456611/
Abstract

In order to develop original and efficient visible light response photocatalysts for degrading organic pollutants in wastewater, new photocatalysts Bi₂GaSbO₇ and Bi₂InSbO₇ were firstly synthesized by a solid-state reaction method and their chemical, physical and structural properties were characterized. Bi₂GaSbO₇ and Bi₂InSbO₇ were crystallized with a pyrochlore-type structure and the lattice parameter of Bi₂GaSbO₇ or Bi₂InSbO₇ was 10.356497 Å or 10.666031 Å. The band gap of Bi₂GaSbO₇ or Bi₂InSbO₇ was estimated to be 2.59 eV or 2.54 eV. Compared with nitrogen doped TiO₂, Bi₂GaSbO₇ and Bi₂InSbO₇, both showed excellent photocatalytic activities for degrading methylene blue during visible light irradiation due to their narrower band gaps and higher crystallization perfection. Bi₂GaSbO₇ showed higher catalytic activity compared with Bi₂InSbO₇. The photocatalytic degradation of methylene blue followed by the first-order reaction kinetics and the first-order rate constant was 0.01470 min, 0.00967 min or 0.00259 min with Bi₂GaSbO₇, Bi₂InSbO₇ or nitrogen doped TiO₂ as a catalyst. The evolution of CO₂ and the removal of total organic carbon were successfully measured and these results indicated continuous mineralization of methylene blue during the photocatalytic process. The possible degradation scheme and pathway of methylene blue was also analyzed. Bi₂GaSbO₇ and Bi₂InSbO₇ photocatalysts both had great potential to purify textile industry wastewater.

摘要

为了开发用于降解废水中有机污染物的新型高效可见光响应光催化剂,首先采用固相反应法合成了新型光催化剂Bi₂GaSbO₇和Bi₂InSbO₇,并对其化学、物理和结构性质进行了表征。Bi₂GaSbO₇和Bi₂InSbO₇以焦绿石型结构结晶,Bi₂GaSbO₇或Bi₂InSbO₇的晶格参数分别为10.356497 Å或10.666031 Å。Bi₂GaSbO₇或Bi₂InSbO₇的带隙估计为2.59 eV或2.54 eV。与氮掺杂TiO₂相比,Bi₂GaSbO₇和Bi₂InSbO₇由于其较窄的带隙和较高的结晶完整性,在可见光照射下对亚甲基蓝的降解均表现出优异的光催化活性。与Bi₂InSbO₇相比,Bi₂GaSbO₇表现出更高的催化活性。以Bi₂GaSbO₇、Bi₂InSbO₇或氮掺杂TiO₂为催化剂时,亚甲基蓝的光催化降解遵循一级反应动力学,一级速率常数分别为0.01470 min⁻¹、0.00967 min⁻¹或0.00259 min⁻¹。成功测量了CO₂的释放和总有机碳的去除,这些结果表明在光催化过程中亚甲基蓝不断矿化。还分析了亚甲基蓝可能的降解方案和途径。Bi₂GaSbO₇和Bi₂InSbO₇光催化剂在净化纺织工业废水方面都具有巨大潜力。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/4496dab2a2b9/materials-09-00801-g014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/cb8d6870dd9c/materials-09-00801-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/76fd0b5230e1/materials-09-00801-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/ebac32abbe78/materials-09-00801-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/5199e999f7ef/materials-09-00801-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/6cfe4b0afc61/materials-09-00801-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/e53142ef6e72/materials-09-00801-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/05fa0a4d2811/materials-09-00801-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/cce8add98015/materials-09-00801-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/a8bc0fa576c8/materials-09-00801-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/51b66ae9b39f/materials-09-00801-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/c8d09dc7886b/materials-09-00801-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/193bb71810d6/materials-09-00801-g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/b15b15616258/materials-09-00801-sch001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/ef6e9209fd71/materials-09-00801-sch002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/37dabb8cba97/materials-09-00801-g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/4496dab2a2b9/materials-09-00801-g014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/cb8d6870dd9c/materials-09-00801-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/76fd0b5230e1/materials-09-00801-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/ebac32abbe78/materials-09-00801-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/5199e999f7ef/materials-09-00801-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/6cfe4b0afc61/materials-09-00801-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/e53142ef6e72/materials-09-00801-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/05fa0a4d2811/materials-09-00801-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/cce8add98015/materials-09-00801-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/a8bc0fa576c8/materials-09-00801-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/51b66ae9b39f/materials-09-00801-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/c8d09dc7886b/materials-09-00801-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/193bb71810d6/materials-09-00801-g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/b15b15616258/materials-09-00801-sch001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/ef6e9209fd71/materials-09-00801-sch002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/37dabb8cba97/materials-09-00801-g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3510/5456611/4496dab2a2b9/materials-09-00801-g014.jpg

相似文献

1
The Structural, Photocatalytic Property Characterization and Enhanced Photocatalytic Activities of Novel Photocatalysts Bi₂GaSbO₇ and Bi₂InSbO₇ during Visible Light Irradiation.新型光催化剂Bi₂GaSbO₇和Bi₂InSbO₇在可见光照射下的结构、光催化性能表征及增强的光催化活性
Materials (Basel). 2016 Sep 27;9(10):801. doi: 10.3390/ma9100801.
2
Synthesis, Structural Property, Photophysical Property, Photocatalytic Property of Novel ZnBiErO₄ under Visible Light Irradiation.新型ZnBiErO₄在可见光照射下的合成、结构性质、光物理性质及光催化性质
Materials (Basel). 2018 Feb 18;11(2):303. doi: 10.3390/ma11020303.
3
Synthesis, property characterization and photocatalytic activity of the novel composite polymer polyaniline/Bi2SnTiO7.新型复合聚合物聚苯胺/ Bi2SnTiO7 的合成、性能表征及光催化活性。
Molecules. 2012 Mar 6;17(3):2752-72. doi: 10.3390/molecules17032752.
4
Synthesis, crystal structure, photodegradation kinetics and photocatalytic activity of novel photocatalyst ZnBiYO4.新型光催化剂ZnBiYO4的合成、晶体结构、光降解动力学及光催化活性
J Environ Sci (China). 2015 Mar 1;29:51-61. doi: 10.1016/j.jes.2014.06.051. Epub 2015 Jan 29.
5
Synthesis, Property Characterization and Photocatalytic Activity of the Polyaniline/BiYTi₂O₇ Polymer Composite.聚苯胺/铋钇钛酸盐聚合物复合材料的合成、性能表征及光催化活性
Polymers (Basel). 2017 Feb 23;9(3):69. doi: 10.3390/polym9030069.
6
Structural, photophysical and photocatalytic properties of new Bi2SbVO7 under visible light irradiation.新型Bi2SbVO7在可见光照射下的结构、光物理和光催化性能
Phys Chem Chem Phys. 2009 Aug 7;11(29):6289-98. doi: 10.1039/b815260h. Epub 2009 May 21.
7
Structural, photophysical and photocatalytic properties of novel Bi2AlVO7.新型Bi2AlVO7的结构、光物理和光催化性质
J Hazard Mater. 2009 May 30;164(2-3):781-9. doi: 10.1016/j.jhazmat.2008.08.088. Epub 2008 Sep 2.
8
Property Characterization and Photocatalytic Activity Evaluation of BiGdO₃ Nanoparticles under Visible Light Irradiation.可见光照射下BiGdO₃纳米颗粒的性质表征及光催化活性评价
Int J Mol Sci. 2016 Sep 8;17(9):1441. doi: 10.3390/ijms17091441.
9
Photocatalytic Water Splitting for Hydrogen Production with Gd₂MSbO₇ (M = Fe, In, Y) Photocatalysts under Visible Light Irradiation.可见光照射下Gd₂MSbO₇(M = Fe、In、Y)光催化剂用于光催化水分解制氢
Materials (Basel). 2014 Dec 24;8(1):16-30. doi: 10.3390/ma8010016.
10
Synthesis, characterization and photocatalytic activity of new photocatalyst ZnBiSbO4 under visible light irradiation.新型光催化剂ZnBiSbO4在可见光照射下的合成、表征及光催化活性
Int J Mol Sci. 2014 May 28;15(6):9459-80. doi: 10.3390/ijms15069459.

引用本文的文献

1
Synthesis and Property Examination of ErFeSbO/BiTiSbO Heterojunction Composite Catalyst and Light-Catalyzed Retrogradation of Enrofloxacin in Pharmaceutical Waste Water under Visible Light Irradiation.铒铁锑酸盐/铋钛锑酸盐异质结复合催化剂的合成与性能研究及可见光照射下制药废水中恩诺沙星的光催化降解
Materials (Basel). 2022 Aug 26;15(17):5906. doi: 10.3390/ma15175906.
2
Synthesis, Performance Measurement of BiSmSbO/ZnBiYO Heterojunction Photocatalyst and Photocatalytic Degradation of Direct Orange within Dye Wastewater under Visible Light Irradiation.BiSmSbO/ZnBiYO异质结光催化剂的合成、性能测定及可见光照射下对染料废水中直接橙的光催化降解
Materials (Basel). 2022 Jun 3;15(11):3986. doi: 10.3390/ma15113986.
3

本文引用的文献

1
Photosensitization of ZnO by AgBr and Ag2CO3: Nanocomposites with tandem n-n heterojunctions and highly enhanced visible-light photocatalytic activity.AgBr 和 Ag2CO3 敏化 ZnO:具有串联 n-n 异质结的纳米复合材料及显著增强的可见光光催化活性。
J Colloid Interface Sci. 2016 Jul 15;474:103-13. doi: 10.1016/j.jcis.2016.04.022. Epub 2016 Apr 19.
2
Eco-friendly and facile integrated biological-cum-photo assisted electrooxidation process for degradation of textile wastewater.用于纺织废水降解的环保且简便的生物兼光辅助电氧化集成工艺。
Water Res. 2016 Apr 15;93:230-241. doi: 10.1016/j.watres.2016.02.041. Epub 2016 Feb 17.
3
WO in suit embed into MIL-101 for enhancement charge carrier separation of photocatalyst.
将WO原位嵌入MIL-101中以增强光催化剂的电荷载流子分离。
Sci Rep. 2019 Mar 19;9(1):4860. doi: 10.1038/s41598-019-41374-z.
4
Photophysical and Photocatalytic Properties of BiSnSbO₆ under Visible Light Irradiation.可见光照射下BiSnSbO₆的光物理和光催化性能
Materials (Basel). 2018 Mar 26;11(4):491. doi: 10.3390/ma11040491.
MoS2/reduced graphene oxide hybrid with CdS nanoparticles as a visible light-driven photocatalyst for the reduction of 4-nitrophenol.
MoS2/还原氧化石墨烯杂化材料负载硫化镉纳米粒子作为可见光驱动光催化剂用于还原 4-硝基苯酚。
J Hazard Mater. 2016 May 15;309:173-9. doi: 10.1016/j.jhazmat.2016.02.021. Epub 2016 Feb 10.
4
Utilization of Metal Sulfide Material of (CuGa)(1-x)Zn(2x)S2 Solid Solution with Visible Light Response in Photocatalytic and Photoelectrochemical Solar Water Splitting Systems.具有可见光响应的(CuGa)(1-x)Zn(2x)S2固溶体金属硫化物材料在光催化和光电化学太阳能水分解系统中的应用
J Phys Chem Lett. 2015 Mar 19;6(6):1042-7. doi: 10.1021/acs.jpclett.5b00137. Epub 2015 Mar 10.
5
Artificial neural network modeling of photocatalytic removal of a disperse dye using synthesized of ZnO nanoparticles on montmorillonite.使用蒙脱石负载合成的氧化锌纳米颗粒对分散染料进行光催化去除的人工神经网络建模。
Spectrochim Acta A Mol Biomol Spectrosc. 2015 Apr 5;140:465-73. doi: 10.1016/j.saa.2014.12.100. Epub 2015 Jan 14.
6
Conducting polypyrrole films as a potential tool for electrochemical treatment of azo dyes in textile wastewaters.以聚吡咯薄膜作为电化学处理纺织废水中偶氮染料的潜在工具。
J Hazard Mater. 2015;283:164-70. doi: 10.1016/j.jhazmat.2014.07.038. Epub 2014 Jul 29.
7
Sonochemical synthesis of Pr-doped ZnO nanoparticles for sonocatalytic degradation of Acid Red 17.用于声催化降解酸性红17的镨掺杂氧化锌纳米颗粒的声化学合成
Ultrason Sonochem. 2015 Jan;22:371-81. doi: 10.1016/j.ultsonch.2014.05.023. Epub 2014 Jun 3.
8
Fabrication of visible-light-driven N-doped ordered mesoporous TiO2 photocatalysts and their photocatalytic applications.可见光驱动的氮掺杂有序介孔二氧化钛光催化剂的制备及其光催化应用。
J Nanosci Nanotechnol. 2014 Apr;14(4):3181-6. doi: 10.1166/jnn.2014.8530.
9
Adsorption of azo dyes using peanut hull and orange peel: a comparative study.采用花生壳和橙皮吸附偶氮染料:比较研究。
Environ Technol. 2014 May-Jun;35(9-12):1436-53. doi: 10.1080/09593330.2013.870234.
10
Biological decolorization of xanthene dyes by anaerobic granular biomass.厌氧颗粒污泥对呫吨染料的生物脱色。
Biodegradation. 2012 Sep;23(5):725-37. doi: 10.1007/s10532-012-9548-7. Epub 2012 Mar 22.