CN107442114A - A kind of Pt loads 3DOMSn4+Adulterate TiO2The preparation of material - Google Patents

A kind of Pt loads 3DOMSn4+Adulterate TiO2The preparation of material Download PDF

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CN107442114A
CN107442114A CN201710617876.4A CN201710617876A CN107442114A CN 107442114 A CN107442114 A CN 107442114A CN 201710617876 A CN201710617876 A CN 201710617876A CN 107442114 A CN107442114 A CN 107442114A
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tio
3dom
photo
composite
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李莉
周黔龙
张鑫悦
安民泽
黄继玮
田宇
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Qiqihar University
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    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/62Platinum group metals with gallium, indium, thallium, germanium, tin or lead
    • B01J23/622Platinum group metals with gallium, indium, thallium, germanium, tin or lead with germanium, tin or lead
    • B01J23/626Platinum group metals with gallium, indium, thallium, germanium, tin or lead with germanium, tin or lead with tin
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/63Pore volume
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/16Reducing
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    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B3/00Hydrogen; Gaseous mixtures containing hydrogen; Separation of hydrogen from mixtures containing it; Purification of hydrogen
    • C01B3/02Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen
    • C01B3/04Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen by decomposition of inorganic compounds, e.g. ammonia
    • C01B3/042Decomposition of water
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02F2305/10Photocatalysts
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
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    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/30Hydrogen technology
    • Y02E60/36Hydrogen production from non-carbon containing sources, e.g. by water electrolysis

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Abstract

Pt is prepared by photo-reduction synthetic method on the basis of glue crystal template the invention discloses one kind and loads 3DOM Sn4+Adulterate TiO2Composite photo-catalyst, belong to chemical industry technical field.Using polystyrene (PS) glueballs as macropore template, using C12H28O4Ti(TTIP)、SnCl4、H2PtCl6·6H2O is raw material, and after vacuum impregnation, three-dimensional ordered macroporous Sn is obtained by calcining4+Adulterate TiO2(it is labeled as 3DOM Sn TiO2);Again after photo-reduction, 3DOM Pt/Sn TiO are obtained2.Its surface topography, microstructure, photocatalytic activity are determined, properties of product improve a lot in terms of the photocatalysis of degrading malachite green and photolysis water hydrogen.

Description

A kind of Pt loads 3DOMSn4+Adulterate TiO2The preparation of material
Technical field
The present invention relates to a kind of Pt load 3DOM Sn prepared on the basis of glue crystal template using photoreduction met hod4+Doping TiO2Composite photo-catalyst, belong to chemical industry technical field.
Background technology
Global energy crisis and environmental problem are more and more prominent, because fossil fuel constantly consumption and non-renewable, hydrogen As cleaning, can store and environmental protection fuel be considered as the most promising substitute of fossil fuel.Although have studied more than 40 years, But TiO2For based photocatalyst because it possesses rich content, cost is low, and stability is high, it is non-toxic the features such as, be still now that light is urged Change research main flow.However, due to higher electron-hole recombination rate so that its conversion efficiency to solar energy is low, in visible ray The low rate and weak absorbing in region are widely applied it to suffer from limitation.Largely report prove, by with compared with The metal nanoparticle (such as Ag, Au, Pt and Pd) of big work function is to TiO2Surface be modified turn into improve photogenerated charge current-carrying The effective way of son separation.Adulterated simultaneously using other elements with TiO2Conduction band and valence band between form intermediate level, extensively It is general to be used to reduce its band gap magnitude, therefore TiO2Absorption edge extend to visible region.
The content of the invention
In order to solve the above problems, it is an object of the invention to provide one kind to utilize photo-reduction on the basis of glue crystal template Method prepares Pt load 3DOM Sn4+Adulterate TiO2Composite photo-catalyst, first, Sn4+The incorporation of ion makes TiO2Possess suitable mixed Synthetic phase structure, what is formed mutually has the raising beneficial to its photocatalytic activity, while light decomposition water can be utilized to produce hydrogen. Two, the specific surface area of material can be expanded by preparing three-dimensional ordered macroporous composite (3DOM), increase the active sites of reaction Point;Meanwhile the macroporous structure of the penetrating openings of 3DOM can reduce the resistance to mass tranfer of material, be advantageous to the diffusion of reactant molecule. Three, by Pt load the photoresponse scope of catalysis can be made to widen to visible region, improve profit of the photochemical catalyst to sunshine Add the flyway of composite light induced electron with the load of rate, and Pt, the multipath migration of this light induced electron from The recombination rate of photo-generate electron-hole pair is substantially reduced, improves the light-catalyzed reaction efficiency of composite.With polystyrene (PS) glueballs is macropore template, using C12H28O4Ti(TTIP)、H2PtCl6·6H2O、SnCl4For raw material, pass through vacuum impregnation Afterwards, 3DOM Sn are obtained by drying and calcination4+Adulterate TiO2Composite photo-catalyst;Pt is supported on by its table by photo-reduction again On face, so as to obtain 3DOM Pt/Sn-TiO2
The technical solution adopted for the present invention to solve the technical problems is:Photoreduction met hod is utilized on the basis of glue crystal template Synthesize Pt load 3DOM Sn4+Adulterate TiO2Composite photo-catalyst, PS glueballs being weighed, quality is 2.000 ± 0.010 g, C12H28O4Ti (TTIP), volume are 1.0 mL, anhydrous SnCl4, volume is 0.1 mL, H2PtCl6·6H2O, volume are 0.3 mL. Take 2.000 ± 0.010 g PS glueballs to be impregnated with methanol, filtered after stirring 30 min, treat its natural drying.2 mL TTIP are taken again It is put into 0.1 mL anhydrous stannic chlorides in beaker, the PS balls handled well is slowly added to after well mixed, then stir 1 h;It is complete It is placed in vacuum drying chamber and vacuumizes after.Finally the solid mixture for completing vacuum is put into Muffle furnace, forged at 600 DEG C Burn 8 h and obtain the prepared three-dimensional ordered macroporous Sn of sample4+Adulterate TiO2(it is labeled as 3DOM Sn-TiO2)。
Take 0. 3000 ± 0.0010 g 3DOM Sn-TiO2In deionized water, 10 min of ultrasound, light is placed on also In former reactor, 3.000 ± 0.010 g vulcanized sodium (as sacrifice agent), 0.3 mL platinum acid chloride solution are separately added into.Mixing After irradiating 1 h using 300 W xenon lamps under vacuum conditions after uniformly, washed 3-4 times with deionized water and ethanol respectively, vacuum is done Dry 10 h obtains composite 3DOM Pt/Sn-TiO2
The beneficial effects of the invention are as follows:Using photoreduction met hod synthesis there is high light catalysis to live on the basis of glue crystal template The 3DOM Pt/Sn-TiO of property2Composite photo-catalyst.Composite is by metal simple-substance Pt, Anatase TiO2And Rutile Type TiO2Composition, and Pt introducing improves absorption of the photochemical catalyst in visible region.3DOM Pt/Sn-TiO2The three-dimensional having has Sequence macroporous structure makes material have larger specific surface area.Compared with P25, composite photo-catalyst is under simulation daylight and visible ray There is preferable light degradation effect to malachite green.In addition, composite catalyst has higher production in alcohol-water mixed solution Hydrogen effect, this is due to Pt introducing, adds the flyway of light induced electron, it is suppressed that light induced electron-sky in composite Cave pair it is compound;Trap is captured at the same time as electronics, new avtive spot is provided for light-catalyzed reaction;Urged so as to improve its light Change activity.
Brief description of the drawings
The present invention will be further described with reference to the accompanying drawings and detailed description.
Fig. 1 is PS glue crystal template surface topography maps.
Fig. 2 is 3DOM Pt/Sn-TiO2Composite photo-catalyst surface topography map.
Fig. 3 is 3DOM Pt/Sn-TiO2The HR-TEM photos of composite photo-catalyst.
Fig. 4 is TiO2、3DOM Sn-TiO2、Pt/Sn-TiO2With 3DOM Pt/Sn-TiO2The XRD of composite photo-catalyst.
Fig. 5 (a) is Pt/Sn-TiO2The N of composite photo-catalyst2Absorption-desorption isotherm.
Fig. 5 (b) is 3DOM Pt/Sn-TiO2The N of composite photo-catalyst2Absorption-desorption isotherm.
Fig. 6 is TiO2、Sn-TiO2、3DOM Sn-TiO2、Pt/Sn-TiO2With 3DOM Pt/Sn-TiO2The UV- of photochemical catalyst Vis schemes.
Fig. 7 is direct light degradation, P25, Sn-TiO under ultraviolet light2、3DOM Sn-TiO2、Pt/Sn-TiO2With 3DOM Pt/ Sn-TiO2Catalytic degradation malachite green kinetic results figure.
Fig. 8 is direct light degradation, P25, Sn-TiO under visible ray2、3DOM Sn-TiO2、Pt/Sn-TiO2With 3DOM Pt/ Sn-TiO2Catalytic degradation malachite green reaction result figure.
Fig. 9 is direct light degradation, P25, Sn-TiO under simulation daylight2、3DOM Sn-TiO2、Pt/Sn-TiO2And 3DOM Pt/Sn-TiO2Catalytic degradation malachite green reaction result figure.
Figure 10 (a) is 3DOM Pt/Sn-TiO2The photolysis water hydrogen result figure in ethanol-water solution.
Figure 10 (b) is P25 and 3DOM Pt/Sn-TiO2The photolysis water hydrogen comparative result figure in ethanol-water solution.
Embodiment
Photoreduction met hod synthesis Pt load 3DOM Sn are utilized on the basis of glue crystal template4+Adulterate TiO2Composite photo-catalyst (3DOM Pt/Sn-TiO2), pipette the C for being purchased from Shanghai Mai Ruier chemical technologies Co., Ltd 99.0%12H28O4Ti (TTIP), body Product is 1.0 mL;With the anhydrous stannic chloride (SnCl for being purchased from Tianjin recovery fine chemistry industry research institute 99.0%4), volume 0.1 ML mixing for standby use.PS templates (are synthesized using the emulsification method of emulsifier-free, and obtain PS glue crystal template by centrifugal drying), Quality is that 2.000 ± 0.010 g are placed in SnCl4-TiO2In solution, the h of vacuum impregnation 12 is carried out after stirring a period of time.Obtain production Thing obtains three using 7 h are calcined at 600 DEG C in the SX-2.5-12 type chamber type electric resistance furnaces of Tianjin Stettlen Instrument Ltd. Tie up ordered big hole Sn4+Adulterate TiO2Composite (is labeled as 3DOM Sn-TiO2).Weigh and produced obtained by 0.3000 ± 0.0010 g Thing 3DOM Sn-TiO2It is placed in Photoreactor, adds 3.000 ± 0.010 g and be purchased from Tianjin recovery fine chemistry industry research institute 99.0% vulcanized sodium (as sacrifice agent), adds the H for being purchased from Shanghai Jing Chun biochemical technologies Co., Ltd2PtCl6·6H2O(Pt Content is that 37.5%), volume is 0.3 mL;Under vacuum conditions using Beijing Bo Feilai Science and Technology Ltd.s after well mixed After PLS-SXE300/300UV xenon sources irradiate 1 h, washed 3-4 times with deionized water and ethanol respectively, be dried in vacuo 10 h Obtain composite 3DOM Pt/Sn-TiO2
3DOM Pt/Sn-TiO2The structure of composite photo-catalyst and performance measurement:
First, surface topography and microstructure
3DOM Pt/Sn-TiO2The surface topography and Micro-Structure Analysis result of sample are shown in Fig. 1-6.It can be clearly viewed by Fig. 1 Arrive, synthesized PS glue crystal templates are neat and orderly in three dimensions, and size is homogeneous.Due in self assembling process by Extruding, so hexagonal shape is presented in PS glueballs.Fig. 2 SEM results show, sample is in aligned orderly, in penetrating big of opening Pore structure, macropore is neat and orderly and is hexagonal shape, and because PS glue crystal template is face-centered cubic arrangement, so can Three apertures are seen at each macropore.Fig. 3 is sample 3DOM Pt/Sn-TiO2HR-TEM photos, as we can see from the figure Pt (111) crystal face, Anatase TiO2(101) crystal face and Rutile Type TiO2(110) crystal face.Fig. 4 is prepared material The XRD of material, from the figure, it can be seen that composite 3DOM Pt/Sn-TiO2In Anatase TiO be present2And Rutile Type TiO2Characteristic peak.Fig. 5 is the N of composite2Absorption-desorption isotherm, as can clearly see from the figure, due to compared with Big specific surface area, the thermoisopleth of three-dimensional ordered macroporous composite significantly move up.Also may be used from Fig. 6 UV-Vis figures To prove, the load of precious metals pt makes photochemical catalyst 3DOM Sn-TiO2There is obvious absorption in visible region.
2nd, photocatalysis performance determines
To synthesized 3DOM Pt/Sn-TiO2Photocatalytic activity carried out degrading malachite green and the light of photolysis water hydrogen is urged Change experiment.In order to evaluate the photocatalysis effect of synthesized composite, from commercially available P25, Sn-TiO2、Pt/Sn-TiO2And 3DOM Sn-TiO2Test as a comparison.
, the influence of different samples to ultraviolet degradation malachite green speed as shown in Figure 7.According to experimental data, according to public affairs Formula1/C t -1/C 0 =kt+bCalculated, wherein,C t Exist for dyestufftConcentration (the mgL at moment-1),C 0 It is dyestuff initial concentration (mg·L-1),kIt is speed constant (min-1),bFor intercept.As seen from Figure 7,1/C t -1/C 0 With the reaction timetBasic linear pass System, the degraded of this explanation dyestuff malachite green follow quasi- second- order reaction kinetics.Decline solution in visible ray and simulation sunshine condition Malachite green result is shown in Fig. 8, Fig. 9,3DOM Pt/Sn-TiO2Degraded of the composite to malachite green shows highest light Catalytic activity, exceed well over commercially available P25.
2、3DOM Pt/Sn-TiO2Shown in photolysis water hydrogen hydrogen output such as Figure 10 (a);Photolysis water hydrogen P25 and 3DOM Pt/Sn-TiO2Different samples are in ethanol-water solution shown in hydrogen output result such as Figure 10 (b).As a result show, 3DOM Pt/Sn- TiO2Composite has excellent hydrogen production potential.

Claims (2)

  1. A kind of 1. Pt load 3DOM Sn4+Adulterate TiO2The photo-reduction preparation method of material, weighs PS glueballs, and quality is 2.000 ± 0.010 g, C12H28O4Ti (TTIP), volume are 1.0 mL, anhydrous SnCl4, volume is 0.1 mL, H2PtCl6·6H2O, volume For 0.3 mL.Take 2.000 ± 0.050 g PS glueballs to be impregnated with methanol, filtered after stirring 30 min, treat its natural drying.Take again 2 mL TTIP and 0.1 mL anhydrous stannic chlorides are put into beaker, and the PS balls handled well are slowly added to after well mixed, are then stirred Mix 1 h;After the completion of be placed in vacuum drying chamber and vacuumize 12 h.The solid mixture for completing vacuum is finally put into Muffle furnace In, 8 h are calcined at 600 DEG C and obtain the prepared three-dimensional ordered macroporous Sn of sample4+Adulterate TiO2(it is labeled as 3DOM Sn- TiO2).Take 0. 3000 ± 0.0010 g 3DOM Sn-TiO2In deionized water, 10 min of ultrasound, photo-reduction is placed on In reactor, 3.000 ± 0.010 g vulcanized sodium (as sacrifice agent), 0.3 mL platinum acid chloride solution are separately added into.Mixing is equal After irradiating 1 h using 300 W xenon lamps under vacuum conditions after even, washed 3-4 times, be dried in vacuo with deionized water and ethanol respectively 10 h obtain composite 3DOM Pt/Sn-TiO2
  2. 2. 3DOM Pt/Sn-TiO according to claim 12The photo-reduction synthetic method of composite photo-catalyst, its feature It is:PS glueballs is weighed, quality is 2.000 ± 0.010 g, C12H28O4Ti (TTIP), volume are 1.0 mL, anhydrous SnCl4, volume For 0.1 mL.The product of preparation is put into vacuum drying chamber by colloid crystal templating and extracts vacuum, institute after the h of vacuum impregnation 12 Obtain product and 7 h are calcined at 600 DEG C, obtain three-dimensional ordered macroporous Sn4+Adulterate TiO2Composite (is labeled as 3DOM Sn- TiO2).The 3DOM Sn-TiO weighed2, quality is 0. 3000 ± 0.0010 g, Na2S·9H2O, quality are 3.000 ± 0.050 G, H2PtCl6·6H2O, volume are 0.3 mL.10 min of ultrasound, are placed in photoreduction device, true after being well mixed After irradiating 1 h using 300 W xenon lamps under dummy status, washed 3-4 times with deionized water and ethanol respectively, 10 h of vacuum drying are obtained Composite 3DOM Pt/Sn-TiO2
CN201710617876.4A 2017-07-26 2017-07-26 A kind of Pt loads 3DOMSn4+Adulterate TiO2The preparation of material Pending CN107442114A (en)

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CN114931949A (en) * 2022-01-20 2022-08-23 浙江理工大学 Photocatalyst for carbon dioxide reduction and preparation method and application thereof

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108479765A (en) * 2018-01-23 2018-09-04 齐齐哈尔大学 Counter opal structure Pt/TiO2-ZrO2Synthetic method
CN114931949A (en) * 2022-01-20 2022-08-23 浙江理工大学 Photocatalyst for carbon dioxide reduction and preparation method and application thereof

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