CN102133524A - Load type Pt/TiO2/Al2O3 fiber composite photocatalyst and preparation method thereof - Google Patents

Load type Pt/TiO2/Al2O3 fiber composite photocatalyst and preparation method thereof Download PDF

Info

Publication number
CN102133524A
CN102133524A CN2011100429850A CN201110042985A CN102133524A CN 102133524 A CN102133524 A CN 102133524A CN 2011100429850 A CN2011100429850 A CN 2011100429850A CN 201110042985 A CN201110042985 A CN 201110042985A CN 102133524 A CN102133524 A CN 102133524A
Authority
CN
China
Prior art keywords
tio
fiber
catalyst
powder
tio2
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.)
Granted
Application number
CN2011100429850A
Other languages
Chinese (zh)
Other versions
CN102133524B (en
Inventor
安保礼
戴樊增
黄小迪
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 Shanghai for Science and Technology
Original Assignee
University of Shanghai for Science and 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 University of Shanghai for Science and Technology filed Critical University of Shanghai for Science and Technology
Priority to CN 201110042985 priority Critical patent/CN102133524B/en
Publication of CN102133524A publication Critical patent/CN102133524A/en
Application granted granted Critical
Publication of CN102133524B publication Critical patent/CN102133524B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Abstract

The invention relates to a load type Pt/TiO2/Al2O3 fiber composite photocatalyst and a preparation method thereof. The catalyst is the composite photocatalyst which takes Al2O3 fiber as a carrier and is formed by loading Pt/TiO2 on the carrier, wherein the mass of the Pt/TiO2 is 10% of that of the Al2O3 fiber; and the mass ratio of the Pt to TiO2 in the Pt/TiO2 is 5:1000. The catalytic activity of the load type photocatalyst is close to that of a photocatalyst dispersed in a solution, and the load type photocatalyst has high catalytic activity and good stability and is reusable. The Al2O3 fiber is light per se, easy to suspend in water and convenient for recycling. The preparation method is simple and highly effective, can be used for large-scale preparation, and has lower cost and practical significance in the application field of treating pollutants with water.

Description

Support type Pt/TiO<sub〉2</sub 〉/Al<sub〉2</sub〉O<sub〉3</sub〉the fiber composite photochemical catalyst and preparation method thereof
Technical field
The present invention relates to a kind of nano-photocatalyst functional material and preparation method thereof, particularly a kind of support type Pt/TiO 2/ Al 2O 3Fiber composite photochemical catalyst and preparation method thereof.
Technical background
China is in industrialization high-speed development period in the last thirty years, and the overall national strength of country and the people's living standard constantly promote, but ecological environment is subjected to serious destruction.Wherein water pollution problems is particularly serious, contains in the waste water and is difficult to biodegradable organic pollution in a large number, as chlorobenzene organic matter, chlorophenol compound etc.Therefore these material serious harm human healths, using low-cost technologies to handle organic pollution in the water is to be badly in need of the significant problem that solves.
Photocatalysis degradation organic contaminant has the reaction condition gentleness, non-secondary pollution, advantage such as processing cost is lower.Owing to itself can not consume in the light-catalyzed reaction, there is not adverse side effect again, therefore become one of important method of administering the water pollution.
Nano titanium oxide is as photochemical catalyst, because of it has the favor that advantages such as photostability, high efficiency, nontoxic, cheapness enjoy people.Yet the main extensive use that exists two problems restricting titanium dioxide optical catalyst in practice: the energy gap of (1) anatase titanium dioxide is 3.2eV, can only absorb the higher ultraviolet ray of energy, and the utilization rate of sunshine is low; (2) nano-titanium dioxide powder easily reunion inactivation, particle itself sedimentation and catalytic effect is descended easily in sewage disposal process, and also suitable difficulty of catalyst recovery, use cost is higher and so cause the secondary pollution problems of water.Therefore, titanium dioxide is carried out modification and load to improve the photocatalysis effect of titanium dioxide.
With the nanometer Pt particle load of trace on the titanium dioxide semiconductor surface, make the electronics and the hole that generate after the illumination distinguish localization on Pt particle and semiconductor TiO 2 particles, separate, oxidation-reduction reaction takes place in each comfortable different position of electronics and hole then.Owing to suppressed the compound of electronics and hole behind the nanometer Pt particle load, thereby improved the photocatalytic activity and the selectivity of nano titanium dioxide photocatalyst greatly.
In the technology of carried titanium dioxide, reported that the carrier of employing has bead, glass plate, porous alumina ceramic film, NACF etc.Usually activity of such catalysts reduces because of the change of specific surface in loading process, and catalyst and carrier-bound poor stability come off easily, and some preparation technology is very complicated, costs an arm and a leg.
Summary of the invention
The object of the present invention is to provide a kind of support type Pt/TiO 2/ Al 2O 3The fiber composite photochemical catalyst.
Two of purpose of the present invention is to provide this Preparation of catalysts method.
For achieving the above object, the present invention adopts following technical scheme:
A kind of support type Pt/TiO 2/ Al 2O 3The fiber composite photochemical catalyst is characterized in that this catalyst is with/Al 2O 3Fiber is a carrier, and load has Pt/TiO 2And the composite photo-catalyst that forms, wherein Pt/TiO 2Quality be Al 2O 310% of quality of fiber; And Pt/TiO 2Middle Pt and TiO 2Mass ratio be 5:1000.
Above-mentioned TiO 2Be anatase-type nanometer titanium dioxide.
A kind ofly prepare above-mentioned support type Pt/TiO 2/ Al 2O 3The fiber composite photochemical catalyst is characterized in that the concrete steps of this method are:
A. titanic oxide nano powder is joined the H that concentration is 0.01mol/L 2PtCl 6In the aqueous solution, and the mol ratio of control Pt and titanium dioxide is 1:480; Add volume ratio V then Methyl alcohol/ V WaterThe methanol aqueous solution of=1:10; Regulator solution pH value to 6.8 ~ 7.0; Shone 3 ~ 5 hours with the 300W xenon lamp after stirring; Obtain compound by centrifugation, washing; This compound drying, cooling back are ground and are obtained dark gray powder; With this dark gray powder 400 ~ 500 0C calcining 2 ~ 4 hours; Obtain the Pt/TiO of grey black 2Powder;
B. with Al 2O 3Fiber is dried 200 ~ 300 with ethanol supersound washing 3 ~ 5 times 0C heat treatment 3 ~ 5 hours; With steps A gained Pt/TiO 2Powder is scattered in the aqueous solution, ultrasonic 5 ~ 15 minutes; With Al 2O 3Fiber impregnation makes Pt/TiO in this solution 2Powder evenly is adsorbed in Al 2O 3Fiber surface; After the drying, 200 ~ 300 0C heat treatment 2 ~ 3 hours obtains support type Pt/TiO 2/ Al 2O 3Fiber catalyst C; Pt/TiO wherein 2Powder and Al 2O 3The quality of fiber ratio is.
The support type Pt/TiO that the present invention is prepared 2/ Al 2O 3The advantage of fiber photocatalyst is: the catalytic activity of gained loaded catalyst of the present invention approaches to be scattered in the photochemical catalyst in the solution, has high catalytic activity, and has good stability, and is reusable.Al 2O 3Fiber itself is very light, suspends in water easily, very is convenient to reclaim.The preparation method is simply efficient, can prepare in a large number, and cost is lower, has practical significance in water treatment contaminant applications field.
Description of drawings
Fig. 1 is the XRD figure of anatase-type nanometer titanium dioxide;
Fig. 2 is Pt/TiO 2The XRD figure of composite catalyst;
Fig. 3 is support type Pt/TiO 2/ Al 2O 3The SEM figure of fiber catalyst;
Fig. 4 is anatase-type nanometer titanium dioxide catalyst and Pt/TiO 2Composite catalyst is to methyl orange the disposal efficiency comparison diagram;
Fig. 5 is Pt/TiO under the different condition 2Composite catalyst and support type Pt/TiO of the present invention 2/ Al 2O 3Fiber catalyst is to methyl orange the disposal efficiency test comparison diagram;
Fig. 6 is Pt/TiO of the present invention 2/ Al 2O 3Fibre composite catalyst light degradation methyl orange replica test.
The specific embodiment
Embodiment one: the cryosol gel process for preparing of anatase-type nanometer titanium dioxide sees also document Sifang Li, * Guoliang Ye, and Guoqin Chen. J. Phys. Chem. C 2009,113,4031, be specially: the 10g butyl titanate is dissolved in the 40ml absolute ether, adds the 12ml glacial acetic acid more inward, fully stirred 1 hour.Dropwise add the mixed solution (10ml water, 5ml glacial acetic acid) of glacial acetic acid and water, fully stirred 1 ~ 3 hour.With the white gels sealing and standing that generates 1 ~ 3 day, remove supernatant liquor, with lower floor's gel 120 0The C oven dry, cooling back grind into powder.Use the deionized water cyclic washing, centrifugal, become neutral until product.With product 100 ~ 120 0The C oven dry, grind into powder is put into crucible with powder then, under air atmosphere, 400 ~ 500 0C calcining 1 ~ 3 hour.Obtain white powder anatase-type nanometer titanium dioxide catalyst A at last, its XRD figure is referring to Fig. 1.
Embodiment two: the H that adds 1.30ml 0.01mol/L in 0.5g embodiment one gained anatase-type nanometer titanium dioxide powders A 2PtCl 6The aqueous solution adds 250ml(V then Methyl alcohol/ V Water=1:10) methanol aqueous solution is with NaOH aqueous solution regulator solution pH value to 6.8 ~ about 7.0.Shone 3 ~ 5 hours with the 300W xenon lamp after stirring.After the illumination, obtain compound by centrifugal, washing.Centrifugal afterproduct is 100 ~ 120 0The C oven dry, the cooling back is ground and is obtained dark gray powder.Under air atmosphere, 400 ~ 500 0C calcining 2 ~ 4 hours.Obtain the 0.5wt% Pt/TiO of grey black 2Fine catalyst B.Referring to accompanying drawing 2.
Embodiment three: with commercial Al 2O 3Fiber is dried with ethanol supersound washing 3 ~ 5 times.Under air atmosphere, 200 ~ 300 0C heat treatment 3 ~ 5 hours.Get the embodiment two gained 0.5wt% Pt/TiO of 20mg 2Powder B is scattered in the aqueous solution, ultrasonic 5 ~ 15 minutes.With Al 2O 3Fiber 200mg is immersed in the solution, makes powder B evenly be adsorbed in Al 2O 3Fiber surface.After the oven dry, under air atmosphere, 200 ~ 300 0C heat treatment 2 ~ 3 hours obtains support type Pt/TiO 2/ Al 2O 3Fiber optic composite catalyst C.Referring to accompanying drawing 3.
The catalytic activity of loaded photocatalyst and stability test
Document Sifang Li, * Guoliang Ye, and Guoqin Chen. J. Phys. Chem. C 2009,113,4031 shows the titanium dioxide optical catalyst Degussa P-25 of catalyst A compared with commerce usefulness, demonstrates higher photocatalytic activity.We measure the photocatalytic activity of catalyst A and catalyst B with the degradation rate size of methyl orange solution.Experiment condition is: it is the methyl orange solution of 5mg/L 100ml that initial concentration is selected in experiment for use.The quality of catalyst A and catalyst B all is 20mg.With 18W ultra violet lamp 2 hours,, detect residue methyl orange concentration with ultraviolet-uisible spectrophotometer, and calculate degradation rate every 15 minutes sample analysis.Experimental result shows that the photocatalytic activity of catalyst B is higher than catalyst A.The methyl orange degradation rate of illumination rear catalyst half an hour A and catalyst B is respectively 44.5% and 74.5%.So Pt/TiO 2Catalyst B demonstrates high photocatalytic activity.(accompanying drawing 4)
The catalytic activity that our continuation comes evaluate catalysts C with the degradation rate size of methyl orange solution.Experiment condition is: it is the methyl orange solution of 5mg/L 100ml that initial concentration is selected in experiment for use.Catalyst 0.5wt% Pt/TiO in the experiment 2The contained quality of powder B all is 20mg.18W ultra violet lamp 2 hours every 15 minutes sample analysis, detects the concentration of residue methyl orange with ultraviolet-uisible spectrophotometer, and calculates degradation rate.Do 3 groups of parallel laboratory tests respectively.
First group of experiment, catalyst B is scattered in the methyl orange solution.The overall optical chemical reaction process is in stirring all the time.Second group of experiment, catalyst B is scattered in the methyl orange solution.The overall optical chemical reaction process is in static condition.The 3rd group of experiment, Pt/TiO 2/ Al 2O 3Fiber catalyst C.Catalyst C is immersed in the methyl orange solution.The overall optical chemical reaction process is in static condition.
Experimental result shows that the degradation rate of illumination three groups of experiment methyl orange solutions after 1 hour all surpasses 90%.Because the water treatment organic pollution is in static environment mostly in actual applications, so support type Pt/TiO 2/ Al 2O 3Fiber catalyst demonstrates high catalytic activity, and catalyst C suspends in water easily simultaneously, easily reclaims, and is reusable, can be used for actual sewage disposal.(accompanying drawing 5)
Pt/TiO 2/ Al 2O 3Behind the fiber catalyst C degraded methyl orange solution, use distilled water immersion 2 hours.After the oven dry, continue to carry out the light degradation test as catalyst, experiment condition is identical, repeats altogether 2 times.Experimental result shows that the degradation rate of illumination 3 test methyl oranges after 1 hour reaches 94.0%, 92.6% and 87.7% respectively, considers factors such as experimental error, experimental result explanation support type Pt/TiO 2/ Al 2O 3Fiber catalyst has stability preferably.(accompanying drawing 6).

Claims (2)

1. support type Pt/TiO 2/ Al 2O 3The fiber composite photochemical catalyst is characterized in that this catalyst is with/Al 2O 3Fiber is a carrier, and load has Pt/TiO 2And the composite photo-catalyst that forms, wherein Pt/TiO 2Quality be Al 2O 310% of quality of fiber; And Pt/TiO 2Middle Pt and TiO 2Mass ratio be 5:1000.
2. one kind prepares support type Pt/TiO according to claim 1 2/ Al 2O 3The fiber composite photochemical catalyst is characterized in that the concrete steps of this method are:
A. titanic oxide nano powder is joined the H that concentration is 0.01mol/L 2PtCl 6In the aqueous solution, and the mol ratio of control Pt and titanium dioxide is 1:480; Add volume ratio V then Methyl alcohol/ V WaterThe methanol aqueous solution of=1:10; Regulator solution pH value to 6.8 ~ 7.0; Shone 3 ~ 5 hours with the 300W xenon lamp after stirring; Obtain compound by centrifugation, washing; This compound drying, cooling back are ground and are obtained dark gray powder; With this dark gray powder 400 ~ 500 0C calcining 2 ~ 4 hours; Obtain the Pt/TiO of grey black 2Powder;
B. with Al 2O 3Fiber is dried 200 ~ 300 with ethanol supersound washing 3 ~ 5 times 0C heat treatment 3 ~ 5 hours; With steps A gained Pt/TiO 2Powder is scattered in the aqueous solution, ultrasonic 5 ~ 15 minutes; With Al 2O 3Fiber impregnation makes Pt/TiO in this solution 2Powder evenly is adsorbed in Al 2O 3Fiber surface; After the drying, 200 ~ 300 0C heat treatment 2 ~ 3 hours obtains support type Pt/TiO 2/ Al 2O 3Fiber catalyst C; Pt/TiO wherein 2Powder and Al 2O 3Quality of fiber is than being 1:10.
CN 201110042985 2011-02-23 2011-02-23 Load type Pt/TiO2/Al2O3 fiber composite photocatalyst and preparation method thereof Expired - Fee Related CN102133524B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN 201110042985 CN102133524B (en) 2011-02-23 2011-02-23 Load type Pt/TiO2/Al2O3 fiber composite photocatalyst and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN 201110042985 CN102133524B (en) 2011-02-23 2011-02-23 Load type Pt/TiO2/Al2O3 fiber composite photocatalyst and preparation method thereof

Publications (2)

Publication Number Publication Date
CN102133524A true CN102133524A (en) 2011-07-27
CN102133524B CN102133524B (en) 2012-12-19

Family

ID=44293529

Family Applications (1)

Application Number Title Priority Date Filing Date
CN 201110042985 Expired - Fee Related CN102133524B (en) 2011-02-23 2011-02-23 Load type Pt/TiO2/Al2O3 fiber composite photocatalyst and preparation method thereof

Country Status (1)

Country Link
CN (1) CN102133524B (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103272588A (en) * 2013-06-13 2013-09-04 南京大学 Recoverable float type Pt-TiO2/ floating bead photocatalyst and preparation method thereof
CN106732816A (en) * 2016-12-08 2017-05-31 湖北工业大学 A kind of Pd/TiO2/ cotton fiber composite formaldehyde room-temperature oxidation catalyst and preparation method thereof
CN109107569A (en) * 2018-09-18 2019-01-01 南通大学 The in-situ synthetic method of the titanium dioxide base nano heterojunction material of supported palladium
CN109126758A (en) * 2018-09-18 2019-01-04 南通大学 The preparation method and its usage of blue titanium dioxide

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101223295A (en) * 2005-06-30 2008-07-16 有限会社K2R Method for formation of alumina coating film, alumina fiber, and gas treatment system comprising the alumina fiber

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101223295A (en) * 2005-06-30 2008-07-16 有限会社K2R Method for formation of alumina coating film, alumina fiber, and gas treatment system comprising the alumina fiber

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
《Catalysis Letters》 19981231 S.T.Srinivas et al. Effect of support modification on the chlorobenzene hydrodechlorination activity on Pt/Al2O3 catalysts 第50卷, *
《Journal of Hazardous Materials》 20090110 Lifeng Wang et al. Study of catalytic decomposition of formaldehyde on Pt/TiO2 alumite catalyst at ambient temperature 第167卷, *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103272588A (en) * 2013-06-13 2013-09-04 南京大学 Recoverable float type Pt-TiO2/ floating bead photocatalyst and preparation method thereof
CN106732816A (en) * 2016-12-08 2017-05-31 湖北工业大学 A kind of Pd/TiO2/ cotton fiber composite formaldehyde room-temperature oxidation catalyst and preparation method thereof
CN109107569A (en) * 2018-09-18 2019-01-01 南通大学 The in-situ synthetic method of the titanium dioxide base nano heterojunction material of supported palladium
CN109126758A (en) * 2018-09-18 2019-01-04 南通大学 The preparation method and its usage of blue titanium dioxide
CN109126758B (en) * 2018-09-18 2023-09-01 南通大学 Preparation method and application of blue titanium dioxide

Also Published As

Publication number Publication date
CN102133524B (en) 2012-12-19

Similar Documents

Publication Publication Date Title
US20200354235A1 (en) Heterojunction composite material consisting of one-dimensional in2o3 hollow nanotube and two-dimensional znfe2o4 nanosheet, and application thereof in water pollutant removal
Li et al. Role of surface/interfacial Cu2+ sites in the photocatalytic activity of coupled CuO− TiO2 nanocomposites
CN102600905B (en) Semiconductor hetero-junction/conductive polymer fiber membrane composite photocatalyst and preparation method thereof
CN103100398B (en) Preparation method of natural zeolite loaded one-dimensional TiO2 nanowire with high catalytic activity
CN107020142B (en) The preparation method of foamed nickel supported carbon nitrogen/reduced graphene photochemical catalyst
CN103480353A (en) Method for synthesis of carbon quantum dot solution by hydrothermal process to prepare composite nano-photocatalyst
CN103433060A (en) Core-shell TiO2/ZnIn2S4 composite photocatalyst and preparation method and application thereof
CN103599802A (en) Preparation method of silver phosphate/graphene nanocomposite
CN103741263B (en) A kind of high-ratio surface porous TiO 2the preparation method of nanofiber
CN107456983A (en) A kind of Ag/AgCl/TiO2Composite photocatalyst material and its preparation method and application
CN104588004A (en) Catalyst for ultraviolet photocatalytic degradation of organic pollutants and preparation method thereof
CN102133524B (en) Load type Pt/TiO2/Al2O3 fiber composite photocatalyst and preparation method thereof
CN106044842A (en) Preparation method and application of sector hydroxyl zinc fluoride
Liu et al. TiOF2/g-C3N4 composite for visible-light driven photocatalysis
CN109985644A (en) The photochemical catalyst and preparation method thereof of organic dyestuff in a kind of efficient degradation water
CN105797762A (en) Photocatalytic ceramsite as well as preparation method and application thereof
CN105664969B (en) A kind of titanium dioxide-platinum-cobaltosic oxide tri compound catalysis material and preparation method thereof
CN106693996A (en) Preparation method and application for bismuth sulfide-bismuth ferrate composite visible-light photocatalyst
CN108654651A (en) A kind of preparation method of the compound gas-phase photocatalysis agent of titanium dioxide/difluoro oxygen titanium
CN103545111A (en) Preparing method and application of P25/TiO2@SiW11Co film
CN103191708B (en) Quantum dot TiO2 loaded SiO2 photocatalyst and preparation method thereof
CN103506104B (en) Carbon-doped TiO2 visible light-responding catalytic film on glass carrier and preparation method thereof
CN106179442A (en) A kind of cerium and nitrogen co-doped titanium dioxide optical catalyst and its preparation method and application
CN102794188A (en) PtC14/Bi2WO6 photocatalyst, and preparation and application thereof
CN104759289A (en) Preparation method of block WS2 sensitized TiO2 visible light catalyst

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
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: 20121219

Termination date: 20160223