CN100406125C - Method for preparing highly active Fe/Sn ion co-doped nano phtocatalyst of titanium dioxide - Google Patents

Method for preparing highly active Fe/Sn ion co-doped nano phtocatalyst of titanium dioxide Download PDF

Info

Publication number
CN100406125C
CN100406125C CNB2006100112394A CN200610011239A CN100406125C CN 100406125 C CN100406125 C CN 100406125C CN B2006100112394 A CNB2006100112394 A CN B2006100112394A CN 200610011239 A CN200610011239 A CN 200610011239A CN 100406125 C CN100406125 C CN 100406125C
Authority
CN
China
Prior art keywords
film
tio
codope
tio2
ion
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
CNB2006100112394A
Other languages
Chinese (zh)
Other versions
CN1799693A (en
Inventor
徐利华
邸云萍
王缓
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.)
University of Science and Technology Beijing USTB
Original Assignee
University of Science and Technology Beijing USTB
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 University of Science and Technology Beijing USTB filed Critical University of Science and Technology Beijing USTB
Priority to CNB2006100112394A priority Critical patent/CN100406125C/en
Publication of CN1799693A publication Critical patent/CN1799693A/en
Application granted granted Critical
Publication of CN100406125C publication Critical patent/CN100406125C/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Catalysts (AREA)

Abstract

The present invention provides a preparation method for a nanometer TiO2 photocatalyst with the codope of high-activity iron ions and stannum ions, which belongs to the technical field of photocatalyst material. The present invention has processing steps: firstly, TiO2 collosol with the codope of Fe<3+> and Sn<4+> is prepared; a TiO2 film with the codope of Fe<3+> and Sn<4+> is prepared. The present invention has the advantages that the prepared TiO2 film with the codope of Fe<3+> and Sn<4+> has the mixed crystal structure of an anatase phase and a rutile phase, the average size of the TiO2 film is 20 nm, the rutile phase is determined to be a solid solution crystal phase formed by that Fe<3+> and Sn<4+> are dissolved in TiO2 crystal lattices in a solid mode; the film plated on a glass basis is transparent and has a smooth surface; the codope of Fe<3+> and Sn<4+> causes the red shift of the absorption edge of a TiO2 photocatalyst film to incident light to a visible region so as to generate a visual light induced photocatalysis effect; the photocatalytic activity of the TiO2 film is obviously increased; compared with a pure nanometer TiO2 film, the photocatalytic degradation rate to methyl orange is increased by two times.

Description

The preparation method of highly active Fe/Sn ion co-doped nano phtocatalyst of titanium dioxide
Technical field
The invention belongs to the photocatalyst material technical field, a kind of preparation method of highly active Fe/Sn ion co-doped nano phtocatalyst of titanium dioxide particularly is provided, has related in particular to a kind of sol-gel preparation technology with iron/tin coblended nano TiO 2 of visible light effect, highlight catalytic active and mixed crystal effect.
Background technology
Nano titanium dioxide belongs to the inorganic new material in environmental protection field, also is the environmental type photocatalyst material that has the exploitation future most.By photochemical catalytic oxidation reduction effect degraded noxious pollutant, and non-secondary pollution, have functions such as wastewater treatment, air cleaning, kill virus and cancer cell, antibiotic, deodorizing, automatically cleaning.
Restriction TiO 2The bottleneck of photocatalyst practical application: the one, the restriction of excitation wavelength is because TiO 2Energy gap be 3.2eV, corresponding excitation wavelength belong to ultraviolet region, and ultraviolet light accounts for less than 5% in big positive energy at 387nm, the photocatalyst material of most economical practicality should be able to utilize visible light part abundant in the sunshine, substitutes expensive artificial ultraviolet source; The 2nd, TiO 2The quick recombination probability height of semiconductor photoproduction electronics and photohole, and the interfacial migration rate of the photoproduction current-carrying that produces is low, has limited TiO 2The photocatalytic activity of photocatalyst.The key technology that addresses the above problem is exactly to TiO 2Photocatalyst carries out modification, and wherein one of the most noticeable method of modifying is exactly the doping of transition metal ions.Mixing of transition metal ions can be at TiO 2Introduce defective locations in the lattice or change TiO 2Degree of crystallinity etc. can be served as the captor of light induced electron or photohole, effectively stop electric charge compound in transfer process, improve quantum yield, thereby influence TiO 2The catalytic activity of photocatalyst; Or at TiO 2Can introduce new energy level in the band, reduce band gap, induce electron transition, make the photoresponse wavelength spread to visible region.
Suspended phase TiO 2Particulate is easy to cohesion in the aqueous solution, be difficult to reclaim, and active ingredient loss is big, has also seriously limited the practicability of photocatalysis technology.Thereby nano-TiO 2Photo-catalyst film again because it has nano effect and high activity, and has theoretical research and actual application value as having reaction and separating bifunctional new material and become the focus of new catalytic material.
Summary of the invention
The support type Fe that the purpose of this invention is to provide a kind of highlight catalytic active and mixed crystal effect 3+/ Sn 4+Ion co-doped nanocrystalline TiO 2The preparation method of photo-catalyst film utilizes metal cations Fe 3+With Sn 4+Synergistic function obviously improve nanocrystalline TiO 2The catalytic activity of photocatalyst.
Processing step of the present invention is:
A.Fe 3+/ Sn 4+The TiO of codope 2The preparation of colloidal sol
With percent by volume is that 15%~20% butyl titanate, 22%~24% absolute ethyl alcohol and 10%~12% acetylacetone,2,4-pentanedione are mixed with homogeneous solution A, according to molar percentage M Sn: M Ti=11.41% and M Fe: M Ti=0.05%~5.00% calculates weighing stannic chloride pentahydrate and nine water ferric nitrates respectively, with the SnCl of aequum 45H 2O and Fe (NO 3) 39H 2O is dissolved in the solution B of 43%~49% absolute ethyl alcohol and the preparation of 2%~3% distilled water, and the pH that drips red fuming nitric acid (RFNA) regulator solution B is 3.15~4.20, again solution B slowly is added drop-wise to the reaction that is hydrolyzed in the solution A, and the control reaction temperature is 30~40 ℃.With the Fe that forms 3+/ Sn 4+The TiO of ion codope 2Colloidal sol was 10~35 ℃ of sealing ageings 4~10 days;
B.Fe 3+/ Sn 4+The TiO of codope 2The preparation of film
Preliminary treatment glass basis before plated film: glass basis soaks with pickle behind 500~550 ℃ of following heat treatment 120~130min in chamber type electric resistance furnace, uses distilled water and absolute ethyl alcohol ultrasonic cleaning then, puts into the baking oven dry for standby at last; The glass basis of cleaning is immersed in the speed of 2~4cm/min in the sol solutions of preparation and leaves standstill 2~5min, treat to lift vertically upward with same pull rate behind the liquid level stabilizing, wet film is at room temperature placed 5~15min, 60~100 ℃ of down dry 10~20min and become gel mould in vacuum drying chamber take out and continue to be coated with a skim down behind 10~35 ℃ of cooling 5~10min again; Repeat above-mentioned coating process cycles prepare 1~10 layer film, plated last tunic after, the vacuum drying chamber of putting into 60~80 ℃ is dry; Speed with 1~2 ℃/min is warmed up to 500~550 ℃ of heat preservation hot processing 120~180min in chamber type electric resistance furnace then, naturally cools to room temperature in stove, obtains the Fe of different dopings 3+/ Sn 4+Ion co-doped TiO 2Photo-catalyst film.
Fe 3+/ Sn 4+Ion co-doped nano-TiO 2Photo-catalyst film photocatalytic activity method of testing:
Select dyestuff methyl orange as the degraded object, the methyl orange of azo structure is a kind of organic compound than difficult degradation, with the simulated wastewater of finished product methyl orange dye preparation as estimating nano-TiO 2The reaction model of film light catalytic activity has certain representativeness.Using the 200ml conical flask as the easy reaction device, is excitation source with the 125W high pressure mercury fluorescent lamp, with the pure TiO of glass tube load 2Film or Fe 3+/ Sn 4+Ion co-doped TiO 2Film is as photochemical catalyst.Photocatalytic activity testing experiment process is: the TiO that puts into the glass tube load in the 200ml conical flask 2The methyl orange aqueous solution of photo-catalyst film and 100ml variable concentrations, different pH, 125W from the ballast high pressure mercury fluorescent lamp apart from conical flask reactor 5~10cm.With air pump bubbling air in methyl orange solution, open light source irradiation different time after several minutes earlier.Measure the absorbance of methyl orange solution with ultraviolet-visible spectrophotometer, change the photocatalytic degradation rate of calculating methyl orange according to the absorbance of methyl orange solution in the maximum absorption wave strong point.Computing formula is D % = A 0 - A A 0 &times; 100 % , A in the formula 0Be the initial absorbance of methyl orange dye solution, A is the reacted absorbance of methyl orange dye solution photocatalytic oxidation degradation.
Utilize X-ray diffraction, AFM, ultraviolet-visible spectrophotometer to study TiO 2The surface topography of photo-catalyst film, phase structure and photocatalytic activity thereof.The invention has the advantages that: the Fe of preparation 3+/ Sn 4+The nano-TiO of codope 2Film has anatase and rutile duplex grain structure mutually, and average grain size is 15~20nm, determines that by analysis rutile is Fe mutually 3+, Sn 4+Be solidly soluted into TiO 2The solid solution crystalline phase that forms in the lattice; The film that is coated with on glass basis is transparent, and surfacing is smooth; Codope Fe 3+/ Sn 4+There is the effect of Synergistic, can produces the visible light-inducing photocatalytic effect, significantly improved TiO 2The photocatalytic activity of film is compared pure nano-TiO 2Film has improved 2 times to the photocatalytic degradation rate of methyl orange.
Description of drawings
Fig. 1 is 500 ℃ of heat treated 0.1%Fe 3+/ 11.41%Sn 4+The TiO of codope 2The XRD figure spectrum of powder.The Fe that this figure explanation obtains through 500 ℃ of heat treatment 120min 3+/ Sn 4+The TiO of codope 2Powder has the mixing crystal formation of Detitanium-ore-type and rutile-type, and TiO 2Crystallite dimension obviously diminishes.
The 0.1%Fe of Fig. 2 on glass basis, being coated with 3+/ 11.41%Sn 4+The TiO of codope 2The AFM photo of film.This figure illustrates that film is evenly smooth, the film surface smoother, and average grain size has hole about 20nm.
Fig. 3 is at doping 11.41%Sn 4+The basis on the mix Fe of different amounts 3+Influence curve to photocatalytic degradation methyl orange.This figure illustrates codope Fe 3+/ Sn 4+Make TiO 2Film significantly strengthens the photocatalytic Degradation of methyl orange, has obviously improved TiO 2The photocatalytic activity of film.
The specific embodiment
Embodiment 1
Drip the 17ml butyl titanate earlier in the 23ml absolute ethyl alcohol, continue magnetic agitation, the back slowly drips the 11ml acetylacetone,2,4-pentanedione as complexing agent, fully obtains homogeneous solution a after the reaction; With 2.00gSnCl 45H 2O and 0.02g Fe (NO 3) 39H 2O is dissolved in the 47ml absolute ethyl alcohol, drips 2ml distilled water and 0.2ml nitric acid again, and magnetic agitation obtains homogeneous solution b.The control reaction temperature is 30 ℃, slowly drips the solution b reaction that is hydrolyzed in the solution a.At last with the Fe that forms 3+/ Sn 4+The TiO of ion codope 2Colloidal sol seals ageing in room temperature.
(1cm * 2.5cm) is immersed in the speed of 4cm/min in the sol solutions of preparation and leaves standstill 2min with the glass tube of pretreated cleaning, treat to lift vertically upward with same pull rate behind the liquid level stabilizing, wet film is at room temperature placed 5min, 60 ℃ of following dryings 10min and become gel mould at least in vacuum drying chamber takes out behind room temperature cooling 5min and continues to be coated with a skim down again.Repeat above-mentioned coating process cycles prepare 3 layer films, plated last tunic after, the vacuum drying chamber of putting into 80 ℃ is dry.Speed with 2 ℃/min is warmed up to 500 ℃ of heat preservation hot processing 120min in chamber type electric resistance furnace then, naturally cools to room temperature in stove, can obtain 0.1%Fe 3+/ 11.41%Sn 4+The TiO of codope 2Photo-catalyst film.
Photocatalytic activity testing experiment: the Fe that in the 200ml conical flask, puts into the glass tube load 3+/ Sn 4+Ion co-doped TiO 2Photo-catalyst film and 100ml concentration are 0.76 * 10 -5The methyl orange aqueous solution of mol/L, pH=3.15 is light source with a 125W from the ballast high pressure mercury fluorescent lamp, and lamp is apart from conical flask reactor 5cm.Use air pump to the methyl orange solution bubbling air earlier, open light source irradiation 30min after several minutes.0.1%Fe in the present embodiment 3+/ 11.41%Sn 4+Codope TiO 2Photo-catalyst film is 89.65% to the photocatalytic degradation rate of methyl orange solution.
Embodiment 2
The processing step of present embodiment is substantially the same manner as Example 1, and that different is Fe (NO 3) 39H 2The doping of O is 0.10g.The photocatalytic activity testing experiment shows the 0.5%Fe of present embodiment 3+/ 11.41%Sn 4+Codope TiO 2Photo-catalyst film is 81.56% to the photocatalytic degradation rate of methyl orange solution.
Comparative example
Earlier drip the 17ml butyl titanate while stirring in the 23ml absolute ethyl alcohol, the back slowly drips the 11ml acetylacetone,2,4-pentanedione as complexing agent, and reacting completely obtains homogeneous solution a; 2ml distilled water and 0.2ml nitric acid are added drop-wise in the 47ml absolute ethyl alcohol, and magnetic agitation obtains homogeneous solution b.The control hydrolysising reacting temperature is 30 ℃, slowly drips the solution b reaction that is hydrolyzed in the solution a while stirring.The pure TiO that will form at last 2Colloidal sol seals ageing in room temperature.
The coating process step is identical with embodiment 1, makes 3 layers of pure TiO at last 2Photo-catalyst film.The photocatalytic activity testing experiment shows the pure TiO of this comparative example 2Photo-catalyst film is 44.76% to the photocatalytic degradation rate of methyl orange solution.

Claims (1)

1. highlight catalytic active Fe 3+/ Sn 4+Ion co-doped nano-TiO 2The preparation method of photo-catalyst film is characterized in that: processing step is:
A.Fe 3+/ Sn 4+The TiO of codope 2The preparation of colloidal sol
17ml butyl titanate, 23ml absolute ethyl alcohol and 11ml acetylacetone,2,4-pentanedione are mixed with homogeneous solution A, according to molar percentage M Sn: M Ti=11.41% and M Fe: M Ti=0.1% calculates weighing stannic chloride pentahydrate and nine water ferric nitrates respectively, with the SnCl of aequum 45H 2O and Fe (NO 3) 39H 2O is dissolved in the 47ml absolute ethyl alcohol and 2ml distilled water is mixed with homogeneous solution B, and the pH that drips red fuming nitric acid (RFNA) regulator solution B is 3.15~4.20, and the control reaction temperature is 30 ℃, and solution B slowly is added drop-wise to the reaction that is hydrolyzed in the solution A, forms Fe 3+/ Sn 4+Ion co-doped TiO 2Colloidal sol was 10~35 ℃ of sealing ageings 4~10 days;
B.Fe 3+/ Sn 4+The TiO of codope 2The preparation of film
Preliminary treatment glass basis before plated film: glass basis soaks with pickle behind 500 ℃ of following heat treatment 120min in chamber type electric resistance furnace, uses distilled water and absolute ethyl alcohol ultrasonic cleaning then, puts into the baking oven dry for standby at last; The glass basis of cleaning is immersed in the speed of 4cm/min in the sol solutions of preparation and leaves standstill 2min, treat to lift vertically upward with same pull rate behind the liquid level stabilizing, wet film is at room temperature placed 5~15min, 60 ℃ of down dry 10~20min and become gel mould in vacuum drying chamber take out and continue to be coated with a skim down behind 10~35 ℃ of cooling 5min again; Repeat above-mentioned coating process cycles prepare 3 layer films, plated last tunic after, the vacuum drying chamber of putting into 80 ℃ is dry; Speed with 2 ℃/min is warmed up to 500 ℃ of heat preservation hot processing 120min in chamber type electric resistance furnace then, naturally cools to room temperature in stove, obtains Fe 3+/ Sn 4+Ion co-doped nano-TiO 2Photo-catalyst film.
CNB2006100112394A 2006-01-19 2006-01-19 Method for preparing highly active Fe/Sn ion co-doped nano phtocatalyst of titanium dioxide Expired - Fee Related CN100406125C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNB2006100112394A CN100406125C (en) 2006-01-19 2006-01-19 Method for preparing highly active Fe/Sn ion co-doped nano phtocatalyst of titanium dioxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNB2006100112394A CN100406125C (en) 2006-01-19 2006-01-19 Method for preparing highly active Fe/Sn ion co-doped nano phtocatalyst of titanium dioxide

Publications (2)

Publication Number Publication Date
CN1799693A CN1799693A (en) 2006-07-12
CN100406125C true CN100406125C (en) 2008-07-30

Family

ID=36810042

Family Applications (1)

Application Number Title Priority Date Filing Date
CNB2006100112394A Expired - Fee Related CN100406125C (en) 2006-01-19 2006-01-19 Method for preparing highly active Fe/Sn ion co-doped nano phtocatalyst of titanium dioxide

Country Status (1)

Country Link
CN (1) CN100406125C (en)

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101791562B (en) * 2010-03-25 2012-06-20 东华大学 Method for preparing ferrum-fluorine-codoped nano-titanium dioxide visible light photocatalyst
CN103861601B (en) * 2012-12-18 2016-03-02 中国科学院大连化学物理研究所 A kind of preparation method of fixing crystalline phase composition different content Fe2O3 doping titanium dioxide
CN104248955A (en) * 2013-06-28 2014-12-31 中国科学院大连化学物理研究所 Method for preparing iron-doped rutile titanium dioxide
CN105016382B (en) * 2014-04-30 2017-01-11 中国科学院化学研究所 Method for preparing pure gold redstone type titanium dioxide nanorod
CN105481079B (en) * 2016-01-08 2018-06-05 中北大学 Modified TiO in a kind of rotating disk reactor2The method of catalyst degradation phenol wastewater
CN106345314A (en) * 2016-09-23 2017-01-25 江苏大学 Porous ferric oxide-titanium oxide-activated carbon complex fiber membrane and preparation method
CN108751741B (en) * 2018-07-11 2020-07-17 燕山大学 Low-emissivity glass with buffer layer and co-doping and preparation method thereof
CN111227427A (en) * 2020-01-16 2020-06-05 浙江荣威鞋业有限公司 Shoe with antibacterial sole and preparation process thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1400185A (en) * 2001-07-31 2003-03-05 武汉理工大学 Method for preparing high-activity titanium dioxide film self-cleaning glass material
CN1404919A (en) * 2002-11-08 2003-03-26 清华大学 Preparation for inferface composite semi-conductor nano thinfilm optical catalyst
CN1436590A (en) * 2002-02-06 2003-08-20 云南大学 Photocatalytic superhydrophilic composite titanium dioxide and tin dioxide film
CN1569714A (en) * 2003-07-24 2005-01-26 中国耀华玻璃集团公司 Photo-catalyzed self-cleaning coating composition and method for preparing same
US20050233899A1 (en) * 2001-12-21 2005-10-20 Toshiaki Anzaki Member having photocatalytic function and method for manufacture thereof

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1400185A (en) * 2001-07-31 2003-03-05 武汉理工大学 Method for preparing high-activity titanium dioxide film self-cleaning glass material
US20050233899A1 (en) * 2001-12-21 2005-10-20 Toshiaki Anzaki Member having photocatalytic function and method for manufacture thereof
CN1436590A (en) * 2002-02-06 2003-08-20 云南大学 Photocatalytic superhydrophilic composite titanium dioxide and tin dioxide film
CN1404919A (en) * 2002-11-08 2003-03-26 清华大学 Preparation for inferface composite semi-conductor nano thinfilm optical catalyst
CN1569714A (en) * 2003-07-24 2005-01-26 中国耀华玻璃集团公司 Photo-catalyzed self-cleaning coating composition and method for preparing same

Non-Patent Citations (6)

* Cited by examiner, † Cited by third party
Title
双元素掺杂对纳米二氧化钛光催化降解甲基橙的影响. 刘崎,陈晓青等.河南化工,第2期. 2004
双元素掺杂对纳米二氧化钛光催化降解甲基橙的影响. 刘崎,陈晓青等.河南化工,第2期. 2004 *
掺杂锡离子对纳米二氧化钛薄膜光催化性能的影响. 邸云萍,徐利华等.云南大学学报(自然科学版),第27卷第5A期. 2005
掺杂锡离子对纳米二氧化钛薄膜光催化性能的影响. 邸云萍,徐利华等.云南大学学报(自然科学版),第27卷第5A期. 2005 *
掺铁TiO2纳米微粒的制备及光催化性能. 陈晓青,杨娟玉等.应用化学,第20卷第1期. 2003
掺铁TiO2纳米微粒的制备及光催化性能. 陈晓青,杨娟玉等.应用化学,第20卷第1期. 2003 *

Also Published As

Publication number Publication date
CN1799693A (en) 2006-07-12

Similar Documents

Publication Publication Date Title
CN100406125C (en) Method for preparing highly active Fe/Sn ion co-doped nano phtocatalyst of titanium dioxide
Liu et al. Enhanced photocatalysis on TiO2 nanotube arrays modified with molecularly imprinted TiO2 thin film
CN103143380B (en) Solvent evaporation method for preparing graphite phase carbon nitride/{001} surface exposed anatase phase titanium dioxide nano composite material
CN102335602B (en) Bismuth tungstate composite photocatalyst, preparation method thereof, and application thereof
Yao et al. Preparation and characterization of a copper phosphotungstate/titanium dioxide (Cu-H3PW12O40/TiO2) composite and the photocatalytic oxidation of high-concentration ammonia nitrogen
CN101385968B (en) Preparation method of photochemical catalyst activated carbon doped titanium dioxide nano material
Kawashima et al. Protonated oxide, nitrided, and reoxidized K2La2Ti3O10 crystals: Visible-light-induced photocatalytic water oxidation and fabrication of their nanosheets
CN101773841A (en) Photocatalyst for water treatment
CN102211033A (en) Method for preparing platinum and nitrogen codoped active carbon supported titanium dioxide photocatalyst
CN1799692A (en) Method for preparing visible light-inducing stannum-doped highly catalytic nano photocatalyst of titanium dioxide
CN103496223B (en) Antifog self-cleaning glass and preparation method thereof
CN103949278A (en) Aluminum product coated with nitrogen-doped graphene/nitrogen-doped TiO2 photo-catalytic material
CN102380366A (en) Bismuth and silicon doped nano titanium dioxide photocatalyst, its preparation and its application
CN101574650A (en) Mesoporous photocatalytic film and preparation method thereof
CN102600865B (en) Photocatalyst for degrading organic dye waste water pollutants and preparation method thereof
Jyothi et al. Novel hydrothermal method for effective doping of N and F into nano Titania for both, energy and environmental applications
Cheng et al. Enhanced visible light photocatalytic activity of mesoporous anatase TiO2 codoped with nitrogen and chlorine
CN104263643B (en) Based on enzymatic-photocatalysis cooperative effect bioreactor and preparation method thereof and the application in degradating organic dye
CN101703925B (en) Thulium doped titanium sol and method for degrading textile organic dirt under visible light
Meng et al. Construction of highly active Fe/N-CQDs/MCN1 photocatalytic self-Fenton system for degradation of ciprofloxacin
CN105350068A (en) Preparation method of porous monocrystalline TiO2 thin film
Kao et al. Characterization, photoelectrochemical properties, and surface wettabilities of transparent porous TiO2 thin films
CN104324743A (en) Preparation method of nitrogen-doped TiO2 nanotube composite Fe2O3 catalyst
CN105664992B (en) A kind of preparation method of nitrogen-doped titanium dioxide nanosheet photocatalyst
Candal et al. New visible-light active semiconductors

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C17 Cessation of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20080730

Termination date: 20120119