CN102744087B - Electrochemistry preparation method for flaky nanometer bismuth oxychloride film photocatalyst - Google Patents

Electrochemistry preparation method for flaky nanometer bismuth oxychloride film photocatalyst Download PDF

Info

Publication number
CN102744087B
CN102744087B CN201210135352.9A CN201210135352A CN102744087B CN 102744087 B CN102744087 B CN 102744087B CN 201210135352 A CN201210135352 A CN 201210135352A CN 102744087 B CN102744087 B CN 102744087B
Authority
CN
China
Prior art keywords
film
biocl
adopting
anode
photocatalytic material
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN201210135352.9A
Other languages
Chinese (zh)
Other versions
CN102744087A (en
Inventor
樊彩梅
李双志
王韵芳
刘晓霞
王琴
张维刚
张小超
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Taiyuan University of Technology
Original Assignee
Taiyuan University of Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Taiyuan University of Technology filed Critical Taiyuan University of Technology
Priority to CN201210135352.9A priority Critical patent/CN102744087B/en
Publication of CN102744087A publication Critical patent/CN102744087A/en
Application granted granted Critical
Publication of CN102744087B publication Critical patent/CN102744087B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Abstract

The invention relates to an electrochemistry preparation method for a flaky nanometer bismuth oxychloride film photocatalyst, and belongs to the technical field of environmental chemical engineering photocatalysis water treatment. The method is characterized by: adopting a Ti substrate as a cathode, adopting a platinum wire electrode as an anode, adopting a Bi(NO3)3.5H2O as an electrolyte solution, and adopting a constant current deposition method to prepare a film A at the cathode; adopting the film A as an anode, adopting a graphite electrode as a cathode, adopting a NaCl solution as an electrolyte solution, and adopting a constant potential oxidation method to prepare a BiOCl film at the anode; and washing with distilled water, and carrying out natural open-air drying. The resulting BiOCl film has characteristics of uniform crystal phase structure, uniform distribution, and flaky nanometer structure. The preparation method of the present invention has the following characteristics that: a process is simple and environmental protection, conditions are mild, an operating period is short, and the prepared film has characteristics of uniform distribution, no toxicity, harmlessness and good photocatalytic activity, and is suitable for photocatalytic degradation of organic pollutants in water or air.

Description

A kind of electrochemical preparation method of flake nano bismoclite film photocatalyst
Technical field
The electrochemical preparation method of a kind of flake nano bismoclite of the present invention film photocatalyst, belongs to environmental chemical engineering photocatalysis technology field, is specifically related to a kind of electrochemical preparation method of flake nano BiOCl film photocatalytic material and the technical scheme of application.
Background technology
Bismoclite (BiOCl) is a kind of indirect band-gap semiconductor, by [Bi 2o 2] layer and free Cl atomic building, thering is the highly layer structure of anisotropic, these two obvious advantages are convenient to the separation in light induced electron-hole, have guaranteed the good stable photocatalytic activity (chemical progress, 2009,21:1734 – 1741) of BiOCl.Therefore,, as a kind of catalysis material that has vast potential for future development in organic pollution process field, BiOCl is subject to showing great attention to of researchers.Many researchers have reported the (X=Cl to BiOX; Br; I) preparation of serial powder photocatalyst, sign and photocatalytic activity research work; by hydrolysis or solvent-thermal method, made BiOX powder; there is the BiOX series powder of Nano microsphere shape microscopic appearance by wide coverage (Rare Metals; 2008,27:243 – 250; Journal of Catalysis, 2009,262:144 – 149; Catalysis Communications, 2011,12:1136 – 1141; Journal of Hazardous Materials, 2011,192:538 – 544; Colloids and Surfaces A:Physicochem.Eng.Aspects, 2011,387:23 – 28).Modification work to BiOX powder catalyst is also day by day in the news.In order to improve the extinction property of BiOCl, make its optical absorption band red shift, the Pare of India etc. have made the BiOCl powder of Mn doping by Hydrolyze method, by sign, learn, mixing of Mn not only makes the band gap of BiOCl be down to 2.74eV by 3.48eV, also make the particle diameter of BiOCl reduce (Applied Surface Science, 2011,258:247 – 253).Zhu etc. have reported the sterilization process of Ag/BiOI to E.coli8099, have made the BiOI (Separation and Purification Technology, 2011) of Ag doping by the hot method of ethylene glycol solvent.In addition, Fe 3o 4, WO 3report (Applied Catalysis B:Environmental, 2009,90:458 – 462 with the composite modified BiOCl powder catalyst such as BOH also studied persons; Applied Catalysis A:General 2011; Catalysis Communications, 2011,16:229 – 233; Journal of Colloid and Interface Science, 2011,356:465 – 472).The advantages such as it is large that powder photocatalyst has specific area, and catalytic activity is good, but aspect practical application, there is intrinsic inferior position, as bad dispersibility, Separation of Solid and Liquid problem and recycling problem etc.Therefore, the research to photocatalyst fixation technology, is having obvious value aspect the actual application problem of solution photocatalysis technology.In existing report, about the immobilization problem of BiOX series photochemical catalyst, be not subject to researchers' common concern, only have report few in number.Cao Sihai etc. provide and have adopted physical vapour deposition (PVD) and chemical oxidization method to prepare the method (CN101724839A of BiOCl film; Nanotechnology; 2009; 20:275702); the film making has flower ball-shaped structure; but in preparation process, need by complicated processes of physical vapor deposition, need special instrument and equipment and high-purity gas as protection gas, the cost of preparing film is higher; operating process is complicated, is unfavorable for suitability for industrialized production.Wu Sujuan etc. have adopted template synthesis BiOCl nano-wire array, and investigated its under UV-irradiation to the degrading activity of rhodamine B (Materials Letters, 2010,64:115 – 118), but the method needs alumina formwork, in preparation process, need higher baking temperature and longer drying time.The employing continuous ionic layer adsorption reaction legal systems such as Zhang Li knows obtain BiOI membrane electrode, and pointed out the application potential (CN101857382A) of membrane electrode in area of solar cell, method is simple, without special reactor and instrument, but need to be through repeatedly just making required film, operating process is comparatively loaded down with trivial details.Existing BiOX process for fixation or physics preparation process that need to be complicated, need to prepare template, or manufacturing cycle is longer, therefore, find out that a kind of reaction condition is gentle, simple and to prepare crystal phase structure unified, the method for the BiOCl film being evenly distributed is necessary.Electrochemical reaction mild condition, without HTHP and special instrument and equipment, cathodic electrodeposition and anodizing at the film photocatalytic material of other kinds (as TiO 2film etc.) in preparation, repeatedly adopted, but also do not find so far to adopt electrochemical method to prepare the report of BiOCl film.
Summary of the invention
The object of the electrochemical preparation method of a kind of flake nano bismoclite of the present invention film photocatalyst is to provide a kind of process for fixation of BiOCl photochemical catalyst, by electrochemical method, prepare a kind of flake nano BiOCl film photocatalytic material, and be applied in the processing of organic pollutant in water.The method is by cathode electrodeposition and two steps of anodic oxidation, on Ti matrix, make BiOCl film, through washing, naturally drying after operation, under room temperature normal pressure, prepared flake nano BiOCl film, the simple process for fixation of molecule catalyst is provided.Raw materials usedly commonly be easy to get, reaction condition is room temperature normal pressure, simple to operate, the cycle is short, be easy to realize suitability for industrialized production.Made BiOCl film has good Photocatalytic activity to methyl orange under ultraviolet light, and film performance is stable, can be recycled.
The electrochemical preparation method of a kind of flake nano bismoclite of the present invention film photocatalytic material, the simple process for fixation that it is characterized in that a kind of molecule catalyst, specifically be a kind of by cathode electrodeposition and two steps of anodic oxidation, on Ti matrix, make BiOCl film, through washing and naturally drying after operation, under room temperature normal pressure, prepare the method for flake nano BiOCl film, its processing step is as follows:
I, cathodic electrodeposition process
Take 1~10 gram and analyze pure Bi (NO 3) 35H 2o is positioned in 50~150mL small beaker, adds 40~140mL distilled water, under magnetic agitation, splashes into dense HCl regulation system pH value to forming settled solution; The oxalic acid solution that employing is 20% through mass fraction titanium sheet matrix after acid etching at 90 ℃ is negative electrode, and platinum electrode is anode, and it is electrolyte that solution is joined by institute, with 2~5mAcm -2for current density galvanostatic deposition 3~10h, form film A;
II, anode oxidation process
Take 1~10 gram of pure NaCl of analysis and be positioned in 50~150mL small beaker, add 40~140mL distilled water, stir and make its dissolving; The prepared film A of the I of take is anode, graphite is negative electrode, it is electrolyte that NaCl solution is joined by institute, at 1~3V constant voltage oxidation, 30~120min, form BiOCl film, after being taken out, cleans with distilled water the BiOCl film making, naturally after drying, make required flake nano BiOCl film, this film consists of Tetragonal BiOCl, there is staggered laminated structure (as shown in Figure 1 and Figure 2), film has good absorption to ultraviolet light, learns that as calculated the band gap of made BiOCl film is about 3.42eV (as shown in Figure 3);
Said method adopts the BiOCl film photocatalytic material make to can be applicable in water in organic Treatment by Photocatalysis Oxidation, particularly in water, trace toxic is harmful in the processing of hardly degraded organic substance, light source used is wavelength 365nm ultraviolet light, reaction condition is: normal temperature and pressure, made BiOCl film photocatalytic material is positioned in aqueous organopolysiloxane over against light source, from reactor bottom, blasts air.
The advantage of the electrochemical preparation method of a kind of flake nano bismoclite of the present invention film photocatalytic material is:
1) adopt first electrochemical method to make BiOCl film photocatalyst;
2) reaction condition is gentle, and whole preparation process can complete under room temperature normal pressure, and electrochemical deposition and oxidation complete under low current density and low-voltage, the flake nano BiOCl film photocatalytic material that adopts simple method to make to be evenly distributed;
3) realize the immobilization of nano-sheet BiOCl, facilitated recycling of Separation of Solid and Liquid and catalyst, and the degraded that had both conveniently been applied to organic pollution in water or in air;
4) made BiOCl film photocatalytic material is evenly distributed, and crystal lattice orientation is obvious, and specific area is larger;
5) made BiOCl film photocatalytic material has good and stable photocatalytic activity under ultraviolet light, and has the longer life-span;
6) made BiOCl film photocatalytic material is conveniently realized additional small electrical field control, thereby can realize the method degradable organic pollutant that adopts photoelectrocatalysis.
Accompanying drawing explanation
Fig. 1 is the SEM picture of the flake nano bismoclite film photocatalytic material of embodiment of the present invention 1 preparation.
Fig. 2 is the XRD spectra of the flake nano bismoclite film photocatalytic material of embodiment of the present invention 1 preparation.
Fig. 3 is the UV-Vis DRS collection of illustrative plates of the flake nano bismoclite film photocatalytic material of embodiment of the present invention 1 preparation.
The specific embodiment
In order to make technical scheme of the present invention clearer, will specifically describe in detail with embodiment below, but content of the present invention is not confined to the scope of cited embodiment.
Embodiment 1
1) cathodic electrodeposition process
Take 3 grams and analyze pure Bi (NO 3) 35H 2o is positioned in 100mL small beaker, adds 90mL distilled water, under magnetic agitation, splashes into dense HCl regulation system pH value to forming settled solution; The oxalic acid solution that employing is 20% through mass fraction titanium sheet matrix after acid etching at 90 ℃ is negative electrode, and platinum filament is anode, and it is electrolyte that solution is joined by institute, with 3mAcm -2for current density galvanostatic deposition 6h, form film 1;
2) anode oxidation process
Take 3 grams of pure NaCl of analysis and be positioned in 100mL small beaker, add 100mL distilled water, stir and make its dissolving; Take film 1 as anode, and graphite is negative electrode, and it is electrolyte that NaCl solution is joined by institute, at 2.0V constant voltage oxidation 60min, forms BiOCl film, after taking-up, with distilled water, cleans, and makes flake nano BiOCl film photocatalytic material after naturally drying;
Institute's made membrane is used for to photocatalytic degradation water methyl orange, reaction condition is: normal temperature and pressure, the methyl orange aqueous solution 50mL of 10mg/L, get the made membrane 1cm * 6cm of institute as photochemical catalyst, from reactor bottom, blast air, at interval of certain hour sample analysis, with UV-VIS spectrophotometry, measure the conversion ratio of methyl orange.Under ultraviolet light, as shown in table 1 to the degradation results of methyl orange in 150min:
Time (min) 0 15 30 45 60 75 90 105 120 135 150
Degradation rate (%) 0 21.8 36.6 56.4 67.3 76.2 84.1 90.1 93.1 96.0 98.0
Embodiment 2
1) cathodic electrodeposition process
Take 2 grams and analyze pure Bi (NO 3) 35H 2o is positioned in 100mL small beaker, adds 90mL distilled water, under magnetic agitation, splashes into dense HCl regulation system pH value to forming settled solution; The oxalic acid solution that employing is 20% through mass fraction titanium sheet matrix after acid etching at 90 ℃ is negative electrode, and platinum filament is anode, and it is electrolyte that solution is joined by institute, with 4mAcm -2for current density galvanostatic deposition 3h, form film 1;
2) anode oxidation process
Take 1 gram of pure NaCl of analysis and be positioned in 100mL small beaker, add 100mL distilled water, stir and make its dissolving; Take film 1 as anode, and graphite is negative electrode, and it is electrolyte that NaCl solution is joined by institute, at 1.5V constant voltage oxidation 120min, form BiOCl film, after the BiOCl film making is taken out, with distilled water, clean, after naturally drying, make flake nano BiOCl film photocatalytic material;
Institute's made membrane is used for to photocatalytic degradation water methyl orange, reaction condition is: normal temperature and pressure, the methyl orange aqueous solution 50mL of 10mg/L, get the made membrane 1cm * 6cm of institute as photochemical catalyst, from reactor bottom, blast air, at interval of certain hour sample analysis, with UV-VIS spectrophotometry, measure the conversion ratio of methyl orange.Under ultraviolet light, as shown in table 2 to the degradation results of methyl orange in 150min:
Time (min) 0 15 30 45 60 75 90 105 120 135 150
Degradation rate (%) 0 15.5 25.6 33.4 40.3 47.2 52.1 54.1 56.1 57.0 58.0
Embodiment 3
1) cathodic electrodeposition process
Take 5 grams and analyze pure Bi (NO 3) 35H 2o is positioned in 100mL small beaker, adds 90mL distilled water, under magnetic agitation, splashes into dense HCl regulation system pH value to forming settled solution; The oxalic acid solution that employing is 20% through mass fraction titanium sheet matrix after acid etching at 90 ℃ is negative electrode, and platinum filament is anode, and it is electrolyte that solution is joined by institute, with 5mAcm -2for current density galvanostatic deposition 8h, form film 1;
2) anode oxidation process
Take 1 gram of pure NaCl of analysis and be positioned in 100mL small beaker, add 100mL distilled water, stir and make its dissolving; Take film 1 as anode, and graphite is negative electrode, and it is electrolyte that NaCl solution is joined by institute, at 1.0V constant voltage oxidation 90min, form BiOCl film, after the BiOCl film making is taken out, with distilled water, clean, after naturally drying, make flake nano BiOCl film photocatalytic material;
Institute's made membrane is used for to photocatalytic degradation water methyl orange, reaction condition is: normal temperature and pressure, the methyl orange aqueous solution 50mL of 10mg/L, get the made membrane 1cm * 6cm of institute as photochemical catalyst, from reactor bottom, blast air, at interval of certain hour sample analysis, with UV-VIS spectrophotometry, measure the conversion ratio of methyl orange.Under ultraviolet light, as shown in table 3 to the degradation results of methyl orange in 150min:
Time (min) 0 15 30 45 60 75 90 105 120 135 150
Degradation rate (%) 0 37 45 57 69 77 82 86 89 89 89
Embodiment 4
1) cathodic electrodeposition process
Take 10 grams and analyze pure Bi (NO 3) 35H 2o is positioned in 100mL small beaker, adds 90mL distilled water, under magnetic agitation, splashes into dense HCl regulation system pH value to forming settled solution; The oxalic acid solution that employing is 20% through mass fraction titanium sheet matrix after acid etching at 90 ℃ is negative electrode, and platinum filament is anode, and it is electrolyte that solution is joined by institute, with 1mAcm -2for current density galvanostatic deposition 10h, form film 1;
2) anode oxidation process
Take 6 grams of pure NaCl of analysis and be positioned in 100mL small beaker, add 100mL distilled water, stir and make its dissolving; Take film 1 as anode, and graphite is negative electrode, and it is electrolyte that NaCl solution is joined by institute, at 2.0V constant voltage oxidation 30min, form BiOCl film, after the BiOCl film making is taken out, with distilled water, clean, after naturally drying, make flake nano BiOCl film photocatalytic material;
Institute's made membrane is used for to photocatalytic degradation water methyl orange, reaction condition is: normal temperature and pressure, the methyl orange aqueous solution 50mL of 10mg/L, get the made membrane 1cm * 6cm of institute as photochemical catalyst, from reactor bottom, blast air, at interval of certain hour sample analysis, with UV-VIS spectrophotometry, measure the conversion ratio of methyl orange.Under ultraviolet light, as shown in table 4 to the degradation results of methyl orange in 150min:
Time (min) 0 15 30 45 60 75 90 105 120 135 150
Degradation rate (%) 0 27.2 42.6 53.4 62.4 69.3 74.2 79.2 83.2 87.1 90.0

Claims (2)

1. the electrochemical preparation method of a flake nano bismoclite film photocatalytic material, the simple process for fixation that it is characterized in that a kind of molecule catalyst, specifically be a kind of by cathode electrodeposition and two steps of anodic oxidation, on Ti matrix, make BiOCl film, through washing and naturally drying after operation, under room temperature normal pressure, prepare the method for flake nano BiOCl film, its processing step is as follows:
Figure 2012101353529100001DEST_PATH_IMAGE002
, cathodic electrodeposition process
Take 1 ~ 10 gram and analyze pure Bi (NO 3) 35H 2o is positioned in 50 ~ 150 mL small beakers, adds 40 ~ 140 mL distilled water, under magnetic agitation, splashes into dense HCl regulation system pH value to forming settled solution; The oxalic acid solution that employing is 20% through mass fraction titanium sheet matrix after acid etching at 90 ℃ is negative electrode, and platinum electrode is anode, and it is electrolyte that solution is joined by institute, with 2 ~ 5 mAcm -2for current density galvanostatic deposition 3 ~ 10 h, form film A;
Figure 2012101353529100001DEST_PATH_IMAGE004
, anode oxidation process
Take 1 ~ 10 gram of pure NaCl of analysis and be positioned in 50 ~ 150 mL small beakers, add 40 ~ 140 mL distilled water, stir and make its dissolving; With
Figure 459175DEST_PATH_IMAGE002
prepared film A is anode, graphite is negative electrode, it is electrolyte that NaCl solution is joined by institute, at 1 ~ 3 V constant voltage oxidation 30 ~ 120 min, forms BiOCl film, after being taken out, cleans with distilled water the BiOCl film making, naturally after drying, make required flake nano BiOCl film, this film consists of Tetragonal BiOCl, has staggered laminated structure, film has good absorption to ultraviolet light, learns that as calculated the band gap of made BiOCl film is about 3.42 eV.
2. adopt the prepared flake nano BiOCl of the electrochemical preparation method film photocatalytic material of a kind of flake nano bismoclite film photocatalytic material described in claim 1, it is characterized in that can be applicable in water in organic Treatment by Photocatalysis Oxidation, particularly in water, trace toxic is harmful in the processing of hardly degraded organic substance, light source used is wavelength 365 nm ultraviolet lights, reaction condition is: normal temperature and pressure, made BiOCl film photocatalytic material is positioned in aqueous organopolysiloxane over against light source, from reactor bottom, blasts air.
CN201210135352.9A 2012-08-22 2012-08-22 Electrochemistry preparation method for flaky nanometer bismuth oxychloride film photocatalyst Expired - Fee Related CN102744087B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210135352.9A CN102744087B (en) 2012-08-22 2012-08-22 Electrochemistry preparation method for flaky nanometer bismuth oxychloride film photocatalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210135352.9A CN102744087B (en) 2012-08-22 2012-08-22 Electrochemistry preparation method for flaky nanometer bismuth oxychloride film photocatalyst

Publications (2)

Publication Number Publication Date
CN102744087A CN102744087A (en) 2012-10-24
CN102744087B true CN102744087B (en) 2014-01-15

Family

ID=47024783

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210135352.9A Expired - Fee Related CN102744087B (en) 2012-08-22 2012-08-22 Electrochemistry preparation method for flaky nanometer bismuth oxychloride film photocatalyst

Country Status (1)

Country Link
CN (1) CN102744087B (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103779102B (en) * 2014-01-17 2016-08-24 许昌学院 Low-temperature in-site builds BiOI/Bi2s3hetero-junction thin-film and flexible optoelectronic chemistry solar cell device
CN107815701B (en) * 2017-10-26 2019-09-27 太原理工大学 A kind of nano-sheet is fluorinated electrochemical preparation method and its application of bismuth thin film
CN108745386A (en) * 2018-04-28 2018-11-06 广州大学 A kind of preparation method of BiOX photocatalyst
CN109518217B (en) * 2018-11-23 2023-08-15 济南大学 Preparation method of cobalt boride-based oxygen evolution catalyst
CN111530481A (en) * 2020-05-26 2020-08-14 广东石油化工学院 Method for rapidly preparing BiOBr nanosheet
CN114669308A (en) * 2022-04-01 2022-06-28 哈尔滨理工大学 BiOCl/Bi preparation by means of electrochemical method in-situ reaction24O31Cl10Method for compounding powder

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101024188A (en) * 2007-02-15 2007-08-29 中国科学院上海硅酸盐研究所 Halogen-oxide photocatalytic material and preparing method
CN101724839B (en) * 2008-10-21 2011-07-27 国家纳米科学中心 Micron/nanoscale BiOCl film material and preparation method thereof
CN101664687A (en) * 2009-09-29 2010-03-10 福州大学 Preparation of visible light catalyst of dye-sensitized bismuth oxyhalogenide and application thereof
CN102068998B (en) * 2011-01-14 2012-12-12 太原理工大学 Preparation and application methods of BiOBr/BiOCl compound photocatalyst
CN102513133B (en) * 2011-10-26 2014-04-16 太原理工大学 Preparation method of flower ball-shaped micro-nano film photocatalytic material

Also Published As

Publication number Publication date
CN102744087A (en) 2012-10-24

Similar Documents

Publication Publication Date Title
Wang et al. Construction of Bi-assisted modified CdS/TiO2 nanotube arrays with ternary S-scheme heterojunction for photocatalytic wastewater treatment and hydrogen production
Yuan et al. Tuning piezoelectric field for optimizing the coupling effect of piezo-photocatalysis
Zou et al. High efficient photodegradation and photocatalytic hydrogen production of CdS/BiVO4 heterostructure through Z-scheme process
Tahir La-modified TiO2/carbon nanotubes assembly nanocomposite for efficient photocatalytic hydrogen evolution from glycerol-water mixture
Zhang et al. SnS2/SnO2 heterostructured nanosheet arrays grown on carbon cloth for efficient photocatalytic reduction of Cr (VI)
Duan et al. TiO2 faceted nanocrystals on the nanofibers: Homojunction TiO2 based Z-scheme photocatalyst for air purification
Yu et al. Synthesis and enhanced photocatalytic activity of a hierarchical porous flowerlike p–n junction NiO/TiO2 photocatalyst
Zhang et al. Electrospun nanofibers of ZnO− SnO2 heterojunction with high photocatalytic activity
Dong et al. Fabrication of CeO2 nanorods for enhanced solar photocatalysts
Liu et al. Recent advances of bismuth oxychloride photocatalytic material: Property, preparation and performance enhancement
Qi et al. Constructing CeO 2/nitrogen-doped carbon quantum dot/gC 3 N 4 heterojunction photocatalysts for highly efficient visible light photocatalysis
CN102744087B (en) Electrochemistry preparation method for flaky nanometer bismuth oxychloride film photocatalyst
Zhai et al. Synthesis of zinc sulfide/copper sulfide/porous carbonized cotton nanocomposites for flexible supercapacitor and recyclable photocatalysis with high performance
CN103949234B (en) Boron doped graphene/TiO 2the preparation method of nanometer rods catalysis material
Wang et al. Preparation and visible-light photocatalytic performances of gC 3 N 4 surface hybridized with a small amount of CdS nanoparticles
Gu et al. Heterojunction photocatalyst of cavity shaped Bi2S3/g-C3N4 for bisphenol a degradation: Regulation of internal electric field via assistance of interfacial functional groups
Xiao et al. Facile synthesis of SnO2 hollow microspheres composed of nanoparticles and their remarkable photocatalytic performance
Liu et al. Superb photocatalytic activity of 2D/2D Cl doped g-C3N4 nanodisc/Bi2WO6 nanosheet heterojunction: Exploration of photoinduced carrier migration in S-scheme heterojunction
Lan et al. Application of flexible PAN/BiOBr-Cl microfibers as self-supporting and highly active photocatalysts for nitrogen fixation and dye degradation
Zhang et al. Synthesis of SnO2/ZnO flowerlike composites photocatalyst for enhanced photocatalytic degradation of malachite green
Feng et al. Effective H2O2-Free photo-Fenton processes over ZnSe nanosheets for photocatalytic degradation of dyes and antibiotics
Cong et al. Fabrication of electrochemically-modified BiVO4-MoS2-Co3O4composite film for bisphenol A degradation
Wang et al. Construction of an S-scheme TiOF2/HTiOF3 heterostructures with abundant OVs and OH groups: Performance, kinetics and mechanism insight
Liu et al. Construction of ternary hollow TiO2-ZnS@ ZnO heterostructure with enhanced visible-light photoactivity
Fang et al. Cu2O decorated carbon-incorporated TiO2 microspheres with enhanced visible light photocatalytic activity

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C53 Correction of patent of invention or patent application
CB03 Change of inventor or designer information

Inventor after: Fan Caimei

Inventor after: Li Shuangzhi

Inventor after: Wang Yunfang

Inventor after: Liu Xiaoxia

Inventor after: Wang Qin

Inventor after: Zhang Weigang

Inventor after: Zhang Xiaochao

Inventor before: Fan Caimei

Inventor before: Liu Xiaoxia

COR Change of bibliographic data

Free format text: CORRECT: INVENTOR; FROM: FAN CAIMEI LIU XIAOXIA TO: FAN CAIMEI LI SHUANGZHI WANG YUNFANG LIU XIAOXIA WANG QIN ZHANG WEIGANG ZHANG XIAOCHAO

C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20140115

Termination date: 20180822