CN102631949A - Modified visible-light responsive titania doped photocatalyst and production method and uses thereof - Google Patents

Modified visible-light responsive titania doped photocatalyst and production method and uses thereof Download PDF

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CN102631949A
CN102631949A CN2011100372320A CN201110037232A CN102631949A CN 102631949 A CN102631949 A CN 102631949A CN 2011100372320 A CN2011100372320 A CN 2011100372320A CN 201110037232 A CN201110037232 A CN 201110037232A CN 102631949 A CN102631949 A CN 102631949A
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titanium dioxide
trifluoroacetic acid
visible light
photochemical catalyst
property
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CN102631949B (en
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孟祥福
李中峰
罗楠
张志维
张颖
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Capital Normal University
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Capital Normal University
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Abstract

The invention relates to a modified visible-light responsive titania doped photocatalyst and production method and uses thereof. The preparation method comprises the following steps that: titanate is hydrolyzed in a trifluoroacetic acid solution and dried to obtain a solid dry gel, and then the solid dry gel is re-dissolved in water, is added with a dopant, and is subjected to hydrothermal treatment to obtain the modified visible-light responsive titania doped photocatalyst. The titania photocatalyst obtained by the preparation method provided by the invention has good photocatalytic activity under irradiation of visible light and high photocatalytic activity. The preparation method is simple, and the equipment is easy to operate. The modified visible-light responsive titania doped photocatalyst can be directly used for photocatalytic degradation of organic pollutants in sewage treatment, and can be mixed with a polymer resin to be used as a composite photocatalyst.

Description

The visible light-responsible titanium dioxide photochemical catalyst of doping vario-property and method for making and purposes
Technical field
The present invention relates to visible light-responsible titanium dioxide photochemical catalyst of doping vario-property and preparation method thereof; And the visible light-responsible titanium dioxide photochemical catalyst of this doping vario-property can directly be used for the organic pollution of photocatalytic degradation sewage, or with the purposes of mixed with polymers as composite photo-catalyst use aspect.
Background technology
Japanese scholar Fujishima found titanium dioxide (TiO since 1972 2) since the brine electrolysis, the light-catalyzed reaction technology has caused that as the potential approach that solves the energy and environmental problem people pay close attention to greatly.TiO 2Have the stable and advantages of environment protection of photocatalytic activity height, chemical property and think the catalysis material of tool development prospect.But, TiO 2Big (the energy gap E of Detitanium-ore-type of semiconductor light-catalyst energy gap broad, band-gap energy g=3.2eV), can only the less ultraviolet light (wavelength is less than 400nm) of absorbing wavelength, and the light of inferior wave band less than 5% also in the sunshine gross energy, solar energy utilization ratio is low.On the other hand, nano-TiO 2Semiconductor light-catalyst light induced electron and hole are very easily compound, and photo-generated carrier efficient is low, and this has greatly limited its practical application.
In order to improve TiO 2The photoresponse scope of photochemical catalyst, the method that adopts at present mainly contain metal ion mixing and method such as nonmetallic ion-doped, for example Chinese invention patent CN1116927 disclose a kind of modified altogether solute doping prepare nano-TiO 2Method; Doped chemical is metals such as iron, copper; The photochemical catalyst particle mean size is 10~20nm, and the trap of interior focusing is 20~25% in the visible region, can utilize visible light sources such as sunshine or indoor incandescent lamp to realize photocatalysis; But the absorption of visible light rate is lower, can not make full use of solar energy.Another Chinese invention patent CN101791562 discloses the preparation method of a kind of iron, fluorin-doped nano-titanium dioxide visible light photocatalyst; But this method need just can obtain iron, fluorin-doped nano-titanium dioxide visible light photocatalyst through high-temperature calcination, and preparation cost is higher.
The titanium dioxide optical catalyst powder forms suspension system with treatment sewage in practical application, post-processed must be passed through methods such as filtrations, centrifugal, flocculation with its Separation and Recovery, and the process complicacy has increased recovery difficult, and cyclic utilization rate is low.Adopt polymer to recycle efficient for the preparing carriers composite photo-catalyst can improve greatly, easy to operate, for the visible light responsive photocatalyst of developing efficient stable provides new thinking.
Summary of the invention
The object of the present invention is to provide a kind of visible light-responsible titanium dioxide photochemical catalyst of doping vario-property.
Another object of the present invention is to provide that a kind of reaction condition is gentle, equipment needed thereby is simple, raw material is easy to get, be applicable to the preparation method of visible light-responsible titanium dioxide photochemical catalyst of the doping vario-property of large-scale production.
A purpose more of the present invention is to provide a kind of purposes of visible light-responsible titanium dioxide photochemical catalyst of doping vario-property; The visible light-responsible titanium dioxide photochemical catalyst of this doping vario-property can directly be used for photocatalytic degradation sewage organic pollution, also can use as composite photo-catalyst with mixed with polymers.
The visible light-responsible titanium dioxide photochemical catalyst of doping vario-property of the present invention is that drying obtains the solid, dry gel with titanate esters hydrolysis in trifluoroacetic acid solution, and is soluble in water again then, adds adulterant, carries out hydrothermal treatment consists and makes.The titanium dioxide optical catalyst that adopts preparation method of the present invention to obtain under radiation of visible light, has good photocatalytic activity and photocatalytic activity is high.Preparation method of the present invention is simple, the device therefor processing ease.The visible light-responsible titanium dioxide photochemical catalyst of this doping vario-property can directly be used for the photocatalytic degradation of sewage disposal organic pollution, also can mix as composite photo-catalyst with fluoropolymer resin and use.
The visible light-responsible titanium dioxide photochemical catalyst of doping vario-property of the present invention; Be that finishing at titanium dioxide has trifluoroacetic acid and contains adulterant in titanium dioxide inside; Wherein the content of trifluoroacetic acid is 40~60wt%, and the content of adulterant is 0~5wt%, and surplus is a titanium dioxide.
Described adulterant is selected from FeCl 3, Fe (NO 3) 3, CuCl 2, Cu (NO 3) 2, Mn (CH 3COO) 2, AgNO 3, CH 3At least a in the group that COOAg etc. formed.
The preparation method of the visible light-responsible titanium dioxide photochemical catalyst of doping vario-property of the present invention may further comprise the steps:
(a) titanate esters is joined hydrolysis in the trifluoroacetic acid solution, wherein titanate esters: the mol ratio of trifluoroacetic acid is 1: 4~1: 10, and stirring at room (mixing time was generally 1~3 hour) obtains brown solution; Drying is also removed volatile accessory substance and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the water; Add adulterant; Carry out hydrothermal treatment consists (time of hydrothermal treatment consists was generally 3~10 hours) then, take out the dry visible light-responsible titanium dioxide photochemical catalyst that obtains doping vario-property; Wherein the content of trifluoroacetic acid is 40~60wt%, and the content of adulterant is 0~5wt%, and surplus is a titanium dioxide.
Described titanate esters is selected from least a in the group that tetraethyl titanate, tetraisopropyl titanate, tetra-n-butyl titanate form.
Described adulterant is selected from FeCl 3, Fe (NO 3) 3, CuCl 2, Cu (NO 3) 2, Mn (CH 3COO) 2, AgNO 3, CH 3At least a in the group that COOAg etc. formed.
The concentration of described trifluoroacetic acid solution is 50~99wt%.
The temperature of described hydrothermal treatment consists is 90~180 ℃.
The visible light-responsible titanium dioxide photochemical catalyst of doping vario-property of the present invention can directly be used for the organic pollution of photocatalytic degradation sewage; Also can use as composite photo-catalyst with mixed with polymers; The organic pollution that is used for photocatalytic degradation sewage, wherein the content of polymer in composite photo-catalyst is 30~50wt%.
Described polymer is selected from least a in the group that polyvinyl alcohol, PETG, polybutylene terephthalate, Merlon, polycaprolactone, polymethyl methacrylate, polycaprolactam, polyvinyl acetate, PVP, polyacrylonitrile, polyacrylic acid etc. are formed.
The advantage of the visible light-responsible titanium dioxide photochemical catalyst of doping vario-property of the present invention is:
(1) preparation condition is gentle, and energy consumption is little, and cost is low, is suitable for large-scale production;
(2) have higher ultraviolet light and visible light catalysis activity simultaneously;
(3) composite photo-catalyst that obtains with mixed with polymers can repetitive cycling use, and is easy to operate.
Description of drawings
Fig. 1. the photoelectron spectroscopy of the visible light-responsible titanium dioxide photochemical catalyst of the doping vario-property of the embodiment of the invention 1.
Fig. 2. the transmission electron microscope photo of the visible light-responsible titanium dioxide photochemical catalyst of the doping vario-property of the embodiment of the invention 2.
The specific embodiment
Embodiment 1
(a) the 10ml tetraethyl titanate is joined in the trifluoroacetic acid solution that 9ml concentration is 99wt%, wherein tetraethyl titanate: the mol ratio of trifluoroacetic acid is 1: 4, and room temperature vigorous stirring 1 hour obtains brown solution; Drying is also removed volatile water byproduct, ethanol and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water; Place autoclave; 90 ℃ of hydrothermal treatment consists are after 10 hours; Take out the dry visible light-responsible titanium dioxide photochemical catalyst that obtains having in the finishing of titanium dioxide the modification of trifluoroacetic acid, wherein the content of trifluoroacetic acid is 40wt%, and the content of titanium dioxide is 60wt%.The photoelectron of the visible light-responsible titanium dioxide photochemical catalyst of gained modification can be as shown in Figure 1.
Embodiment 2
(a) the 10ml tetra-n-butyl titanate is joined in the trifluoroacetic acid solution that 44.4ml concentration is 50wt%, wherein tetra-n-butyl titanate: the mol ratio of trifluoroacetic acid is 1: 10, and room temperature vigorous stirring 3 hours obtains brown solution; Drying is also removed volatile water byproduct, butanols and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water; Place autoclave; 180 ℃ of hydrothermal treatment consists are after 3 hours; Take out the dry visible light-responsible titanium dioxide photochemical catalyst that obtains having in the finishing of titanium dioxide the modification of trifluoroacetic acid, wherein the content of trifluoroacetic acid is 60wt%, and the content of titanium dioxide is 40wt%.The transmission electron microscope photo of the visible light-responsible titanium dioxide photochemical catalyst of gained modification is as shown in Figure 2.
Embodiment 3
(a) the 10ml tetraisopropyl titanate is joined in the trifluoroacetic acid solution that 16.7ml concentration is 80wt%, wherein tetra-n-butyl titanate: the mol ratio of trifluoroacetic acid is 1: 6, and room temperature vigorous stirring 2 hours obtains brown solution; Drying is also removed volatile water byproduct, isopropyl alcohol and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water; Place autoclave; 150 ℃ of hydrothermal treatment consists are after 5 hours; Take out the dry visible light-responsible titanium dioxide photochemical catalyst that obtains having in the finishing of titanium dioxide the modification of trifluoroacetic acid, wherein the content of trifluoroacetic acid is 44wt%, and the content of titanium dioxide is 56wt%.
The visible light-responsible titanium dioxide photochemical catalyst of the 0.2g modification that (c) step (b) is obtained joins in the rhodamine B aqueous solution that 50ml concentration is 30mg/L; Through solar radiation after 4 hours; The concentration of rhodamine B is reduced to 0.5mg/L, and the photocatalytic degradation rate of rhodamine B reaches 98.3%.
Embodiment 4
(a) mixture with 5ml tetraisopropyl titanate and 5ml tetra-n-butyl titanate joins in the trifluoroacetic acid solution that 10ml concentration is 99wt%; Tetra-n-butyl titanate wherein: tetraisopropyl titanate: the mol ratio of trifluoroacetic acid is 1: 1: 8; Room temperature vigorous stirring 2 hours obtains brown solution; Drying is also removed volatile water byproduct, isopropyl alcohol, n-butanol and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water, adds 0.05gFeCl 3Adulterant places autoclave, and 150 ℃ of hydrothermal treatment consists were taken out drying and obtained trifluoroacetic acid being arranged and containing FeCl in titanium dioxide inside in the finishing of titanium dioxide after 3 hours 3The visible light-responsible titanium dioxide photochemical catalyst of doping vario-property, wherein the content of trifluoroacetic acid is 40wt%, the content of adulterant is 5wt%, the content of titanium dioxide is 55wt%.
The visible light-responsible titanium dioxide photochemical catalyst of the 0.2g doping vario-property that (c) step (b) is obtained joins in the rhodamine B aqueous solution that 50ml concentration is 30mg/L; Through solar radiation after 4 hours; The concentration of rhodamine B is reduced to 0.2mg/L, and the photocatalytic degradation rate of rhodamine B reaches 99.3%.
Embodiment 5
(a) the 10ml tetra-n-butyl titanate is joined in the trifluoroacetic acid solution that 22.2ml concentration is 50wt%, wherein tetra-n-butyl titanate: the mol ratio of trifluoroacetic acid is 1: 5, and room temperature vigorous stirring 3 hours obtains brown solution; Drying is also removed volatile water byproduct, n-butanol and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water, adds 0.01g CuCl 2Adulterant places autoclave, and 150 ℃ of hydrothermal treatment consists were taken out drying and obtained trifluoroacetic acid being arranged and containing CuCl in titanium dioxide inside in the finishing of titanium dioxide after 3 hours 2The visible light-responsible titanium dioxide photochemical catalyst of doping vario-property, wherein the content of trifluoroacetic acid is 44wt%, the content of adulterant is 1wt%, the content of titanium dioxide is 55wt%.
The visible light-responsible titanium dioxide photochemical catalyst of the doping vario-property that (c) 1g step (b) is obtained is distributed in the 20ml water; Getting the 0.8g polyvinyl alcohol is dissolved in the 30ml water; With the two mixing and stirring, obtain composite photo-catalyst after the drying, wherein the content of polymer is 44.4wt%.
(d) composite photo-catalyst that 0.2g step (c) is obtained joins in the rhodamine B aqueous solution that 50ml concentration is 30mg/L, and after 6 hours, the concentration of rhodamine B is reduced to 1.2mg/L through solar radiation, and the photocatalytic degradation rate of rhodamine B reaches 96%.
Embodiment 6
(a) the 10ml tetra-n-butyl titanate is joined in the trifluoroacetic acid solution that 11.2ml concentration is 99wt%, wherein tetra-n-butyl titanate: the mol ratio of trifluoroacetic acid is 1: 5, and room temperature vigorous stirring 3 hours obtains brown solution; Drying is also removed volatile water byproduct, n-butanol and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water, adds 0.01g AgNO 3With 0.01g CH 3The COOAg adulterant places autoclave, and 150 ℃ of hydrothermal treatment consists were taken out drying and obtained trifluoroacetic acid being arranged and containing AgNO in titanium dioxide inside in the finishing of titanium dioxide after 3 hours 3And CH 3The visible light-responsible titanium dioxide photochemical catalyst of the doping vario-property of COOAg, wherein the content of trifluoroacetic acid is 44wt%, and the content of adulterant is 2wt%, and the content of titanium dioxide is 54wt%.
The visible light-responsible titanium dioxide photochemical catalyst of the doping vario-property that (c) 1g step (b) is obtained is distributed in the 20ml water; Getting the 0.6g PVP is dissolved in the 20ml water; With the two mixing and stirring, obtain composite photo-catalyst after the drying, wherein the content of polymer is 37.5wt%.
(d) composite photo-catalyst that 0.2g step (c) is obtained joins in the methyl orange aqueous solution that 50ml concentration is 30mg/L, and after 6 hours, the concentration of methyl orange is reduced to 0.6mg/L through solar radiation, and the photocatalytic degradation rate of methyl orange reaches 98%.
Embodiment 7
(a) mixture with 5ml tetraisopropyl titanate and 5ml tetra-n-butyl titanate joins in the trifluoroacetic acid solution that 10ml concentration is 99wt%; Tetra-n-butyl titanate wherein: tetraisopropyl titanate: the mol ratio of trifluoroacetic acid is 1: 1: 8; Room temperature vigorous stirring 2 hours obtains brown solution; Drying is also removed volatile water byproduct, isopropyl alcohol, n-butanol and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water, adds 0.01gFeCl 3And 0.01gCuCl 2Adulterant places autoclave, and 150 ℃ of hydrothermal treatment consists were taken out drying and obtained trifluoroacetic acid being arranged and containing FeCl in titanium dioxide inside in the finishing of titanium dioxide after 3 hours 3And CuCl 2The visible light-responsible titanium dioxide photochemical catalyst of doping vario-property, wherein the content of trifluoroacetic acid is 40wt%, the content of adulterant is 2wt%, the content of titanium dioxide is 58wt%.
The visible light-responsible titanium dioxide photochemical catalyst of the doping vario-property that (c) 1g step (b) is obtained is distributed in the 20ml oxolane; Getting the 0.5g PETG is dissolved in the 20ml trifluoroacetic acid; Other gets the 0.5g polymethyl methacrylate and is dissolved in the 20ml oxolane; With three's mixing and stirring, obtain composite photo-catalyst after the drying, wherein the content of polymer is 50wt%.
(d) composite photo-catalyst that 0.2g step (c) is obtained joins in the aqueous solution of methylene blue that 50ml concentration is 30mg/L, and after 5 hours, the concentration of methylene blue is reduced to 0.8mg/L through solar radiation, and the photocatalytic degradation rate of methyl orange reaches 97.3%.
Embodiment 8
(a) the 10ml tetra-n-butyl titanate is joined in the trifluoroacetic acid solution that 14.8ml concentration is 90wt%, wherein tetra-n-butyl titanate: the mol ratio of trifluoroacetic acid is 1: 6, and room temperature vigorous stirring 3 hours obtains brown solution; Drying is also removed volatile water byproduct, n-butanol and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water, adds 0.01gCuCl 2Adulterant places autoclave, and 150 ℃ of hydrothermal treatment consists were taken out drying and obtained trifluoroacetic acid being arranged and containing CuCl in titanium dioxide inside in the finishing of titanium dioxide after 3 hours 2The visible light-responsible titanium dioxide photochemical catalyst of doping vario-property, wherein the content of trifluoroacetic acid is 44wt%, the content of adulterant is 1wt%, the content of titanium dioxide is 55wt%.
The visible light-responsible titanium dioxide photochemical catalyst of the doping vario-property that (c) 1g step (b) is obtained is distributed in the 20ml water; Getting the 0.43g polyvinyl alcohol is dissolved in the 30ml water; With the two mixing and stirring, obtain composite photo-catalyst after the drying, wherein the content of polymer is 30wt%.
(d) composite photo-catalyst that 0.2g step (c) is obtained joins in the rhodamine B aqueous solution that 50ml concentration is 30mg/L, and after 4 hours, the concentration of rhodamine B is reduced to 1.6mg/L through solar radiation, and the photocatalytic degradation rate of rhodamine B reaches 94.7%.
Embodiment 9
(a) the 10ml tetraethyl titanate is joined in the trifluoroacetic acid solution that 9ml concentration is 99wt%, wherein tetraethyl titanate: the mol ratio of trifluoroacetic acid is 1: 4, and room temperature vigorous stirring 1 hour obtains brown solution; Drying is also removed volatile water byproduct, ethanol and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water; Place autoclave; 180 ℃ of hydrothermal treatment consists are after 5 hours; Take out the dry visible light-responsible titanium dioxide photochemical catalyst that obtains having in the finishing of titanium dioxide the modification of trifluoroacetic acid, wherein the content of trifluoroacetic acid is 40wt%, and the content of titanium dioxide is 60wt%.
The visible light-responsible titanium dioxide photochemical catalyst of the modification that (c) 0.5g step (b) is obtained is distributed in the 20ml water; Getting the 0.5g polyvinyl alcohol is dissolved in the 30ml water; With the two mixing and stirring, obtain composite photo-catalyst after the drying, wherein the content of polymer is 50wt%.
(d) composite photo-catalyst that 0.2g step (c) is obtained joins in the rhodamine B aqueous solution that 50ml concentration is 30mg/L, and after 4 hours, the concentration of rhodamine B is reduced to 1.6mg/L through solar radiation, and the photocatalytic degradation rate of rhodamine B reaches 94.7%.
Embodiment 10
(a) the 10ml tetra-n-butyl titanate is joined in the trifluoroacetic acid solution that 13.8ml concentration is 80wt%, wherein tetra-n-butyl titanate: the mol ratio of trifluoroacetic acid is 1: 5, and room temperature vigorous stirring 3 hours obtains brown solution; Drying is also removed volatile water byproduct, n-butanol and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that 1g step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the 20ml water, adds 0.01g CuCl 2And 0.01gFeCl 3Adulterant places autoclave, and 180 ℃ of hydrothermal treatment consists were taken out drying and obtained trifluoroacetic acid being arranged and containing CuCl in titanium dioxide inside in the finishing of titanium dioxide after 5 hours 2And FeCl 3The visible light-responsible titanium dioxide photochemical catalyst of doping vario-property, wherein the content of trifluoroacetic acid is 43wt%, the content of adulterant is 2wt%, the content of titanium dioxide is 55wt%.
The visible light-responsible titanium dioxide photochemical catalyst of the doping vario-property that (c) 1g step (b) is obtained is distributed in the 20ml water; Getting 0.45g polyvinyl alcohol and 0.45g polyacrylic acid is dissolved in respectively in the 30ml water; With three's mixing and stirring; Obtain composite photo-catalyst after the drying, wherein the content of polymer is 47.4wt%.
(d) composite photo-catalyst that 0.2g step (c) is obtained joins in the methyl orange aqueous solution that 50ml concentration is 30mg/L, and after 4 hours, the concentration of methyl orange is reduced to 0.6mg/L through solar radiation, and the photocatalytic degradation rate reaches 98%.

Claims (10)

1. the visible light-responsible titanium dioxide photochemical catalyst of a doping vario-property; It is characterized in that: described photochemical catalyst is that the finishing at titanium dioxide has trifluoroacetic acid and contains adulterant in titanium dioxide inside; Wherein the content of trifluoroacetic acid is 40~60wt%; The content of adulterant is 0~5wt%, and surplus is a titanium dioxide.
2. the visible light-responsible titanium dioxide photochemical catalyst of doping vario-property according to claim 1, it is characterized in that: described adulterant is selected from FeCl 3, Fe (NO 3) 3, CuCl 2, Cu (NO 3) 2, Mn (CH 3COO) 2, AgNO 3, CH 3At least a in the group that COOAg formed.
3. the preparation method of the visible light-responsible titanium dioxide photochemical catalyst of a doping vario-property according to claim 1 and 2 is characterized in that, this method may further comprise the steps:
(a) titanate esters is joined hydrolysis in the trifluoroacetic acid solution, wherein titanate esters: the mol ratio of trifluoroacetic acid is 1: 4~1: 10, and stirring at room obtains brown solution; Drying is also removed volatile accessory substance and excessive trifluoroacetic acid, obtains the titanium dioxide xerogel that finishing has trifluoroacetic acid;
(b) finishing that step (a) is obtained has the titanium dioxide xerogel of trifluoroacetic acid to be dissolved in the water, and adds adulterant, carries out hydrothermal treatment consists then, takes out the dry visible light-responsible titanium dioxide photochemical catalyst that obtains doping vario-property; Wherein the content of trifluoroacetic acid is 40~60wt%, and the content of adulterant is 0~5wt%, and surplus is a titanium dioxide.
4. preparation method according to claim 3 is characterized in that: described titanate esters is selected from least a in the group that tetraethyl titanate, tetraisopropyl titanate, tetra-n-butyl titanate form.
5. preparation method according to claim 3 is characterized in that: described adulterant is selected from FeCl 3, Fe (NO 3) 3, CuCl 2, Cu (NO 3) 2, Mn (CH 3COO) 2, AgNO 3, CH 3At least a in the group that COOAg formed.
6. preparation method according to claim 3 is characterized in that: the concentration of described trifluoroacetic acid solution is 50~99wt%.
7. preparation method according to claim 3 is characterized in that: the temperature of described hydrothermal treatment consists is 90~180 ℃.
8. according to claim 3 or 7 described preparation methods, it is characterized in that: the time of described hydrothermal treatment consists is 3~10 hours.
9. the purposes of the visible light-responsible titanium dioxide photochemical catalyst of a doping vario-property according to claim 1 and 2, it is characterized in that: the visible light-responsible titanium dioxide photochemical catalyst of described doping vario-property directly is used for the organic pollution of photocatalytic degradation sewage; Or the visible light-responsible titanium dioxide photochemical catalyst and the mixed with polymers of described doping vario-property use as composite photo-catalyst, is used for the organic pollution of photocatalytic degradation sewage, and wherein the content of polymer in composite photo-catalyst is 30~50wt%.
10. purposes according to claim 9 is characterized in that: described polymer is selected from least a in the group that polyvinyl alcohol, PETG, polybutylene terephthalate, Merlon, polycaprolactone, polymethyl methacrylate, polycaprolactam, polyvinyl acetate, PVP, polyacrylonitrile, polyacrylic acid form.
CN 201110037232 2011-02-12 2011-02-12 Modified visible-light responsive titania doped photocatalyst and production method and uses thereof Expired - Fee Related CN102631949B (en)

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