CN105771951A - Carbon-titanium composite nanofiber supported catalyst and preparation method and application thereof - Google Patents

Carbon-titanium composite nanofiber supported catalyst and preparation method and application thereof Download PDF

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CN105771951A
CN105771951A CN201610153723.4A CN201610153723A CN105771951A CN 105771951 A CN105771951 A CN 105771951A CN 201610153723 A CN201610153723 A CN 201610153723A CN 105771951 A CN105771951 A CN 105771951A
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carbon
titanium composite
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CN105771951B (en
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高翔
竺新波
郑成航
岑可法
骆仲泱
倪明江
周劲松
于馨凝
翁卫国
吴卫红
张涌新
宋浩
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Zhejiang University ZJU
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/18Carbon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8668Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
    • BPERFORMING OPERATIONS; TRANSPORTING
    • 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
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
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    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/16Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/20Vanadium, niobium or tantalum
    • B01J23/22Vanadium
    • 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
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/58Fabrics or filaments
    • 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
    • B01J35/61310-100 m2/g
    • 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
    • B01J35/615100-500 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/06Polluted air

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Abstract

The invention relates to a carbon-titanium composite nanofiber supported catalyst and a preparation method and application thereof. By carbon-titanium composite nanofibers serving as supporters and transition metal oxides serving as active components, the active components are led into a spinning solution in situ to obtain the catalyst with supporting capacity being 0-50%. The preparation method includes: preparing a precursor solution containing carbon precursors, titanium precursors and the active components; obtaining nanofibers of precursor components according to an electrospinning method; performing high-temperature calcination in a nitrogen atmosphere. The catalyst which takes the carbon-titanium composite nanofibers as the supporters integrates advantages of large specific area and favorable low-temperature activity of carbon supporters and advantages of property stability and large quantity of acid sites of TiO2 supporters and has a wide catalytic temperature window and favorable reaction activity. In addition, the preparation method is simple in process, the raw materials are easy to acquire, and the carbon-titanium composite nanofiber supported catalyst is a novel high-efficiency low-cost catalyst applicable to catalytic oxidation removal of volatile organic pollutants such as ketones and aldehydes.

Description

The loaded catalyst and its preparation method and application being carrier with carbon titanium composite nano fiber
Technical field
The invention belongs to chemical catalyst and preparing technical field thereof, concretely relate to a kind of loaded catalyst and its preparation method and application being carrier with carbon titanium composite nano fiber.
Background technology
China is an energy-consuming big country, primary energy consumption structure based on coal, coal combustion generate SO2、NOx, hydrargyrum, two English, the pollutant such as volatile organic matter make China become one of country the most serious of atmospheric pollution in the world.Wherein volatile organic matter (VolatileOrganicCompounds, it is called for short VOCs) refer to that under room temperature, saturated vapor pressure, more than the boiling point organic compound lower than 260 DEG C under 70Pa, normal pressure, mainly includes aromatic hydrocarbon, aliphatic hydrocarbon, halogenated hydrocarbons, alcohols, aldehydes, ketone and esters etc..The discharge of VOCs not only results in the environmental problems such as greenhouse effect, depletion of the ozone layer, photochemical fog, but also health can produce serious harm.The General Office of the State Council proposes to carry out volatile organic matter prevention and cure of pollution work from State-level to first official for 2010 in " about advancing atmospheric pollution groupcontrol job guide suggestion ", is classified as the priority pollutant of atmospheric pollution groupcontrol.Therefore, the discharge how efficiently and economically reducing volatile organic matter (VOCs) has great significance for administering China's atmospheric pollution.
In the control technology of VOCs, introduce the catalysed oxidation processes after catalyst owing to having the significant advantages such as can carry out, removal efficiency is higher, applied widely, operation is simple at low concentrations, thus become most one of removal methods with application prospect at present.In prior art, the carrier of catalyst is substantially the employing organic material such as metal-oxide or graphite, activated carbon, resin.Chinese patent CN102824909A discloses a kind of with Al2O3For carrier, the catalyst being active component with precious metals pd, the oxidation reaction of the VOCs such as benzene,toluene,xylene, ethyl acetate, ethanol, propane is had significantly high catalysis activity.Chinese patent CN104138756A discloses a kind of loaded catalyst RTCC-1 being carrier with TSC-1 mesoporous carbon, and active component is a kind of in conjunction with one or more metal-oxides in copper oxide, cerium oxide, zirconium oxide, silicon oxide, aluminium oxide in Pd or Pt noble metal.But in above-mentioned catalyst, although with the organic material such as mesoporous carbon, graphite be carrier catalyst there is good low temperature active, but owing to carrier surface acid site is less, the carrying out of catalytic reaction is had certain restriction;With Al2O3、TiO2Deng the catalyst that metal-oxide is carrier, there is when high temperature good reactivity, but the catalysis activity when low-temp reaction is poor.Although and the introducing of noble metal active component enhances reactivity in catalyst, but also improving the preparation cost of catalyst, hardly resulting in and being widely applied.
Therefore, how to prepare and there is wider reaction temperature window, good catalysis activity, prepare catalyst simple, with low cost and become in current VOCs catalytic eliminating technology most one of direction with Research Prospects.
Summary of the invention
In order to solve the deficiencies in the prior art, the invention provides a kind of loaded catalyst and its preparation method and application being carrier with carbon titanium composite nano fiber.Catalyst of the present invention is big in combination with carbon carrier specific surface area, low temperature active is good advantage and TiO2The advantage that support is stable, sour site is many, there is wider catalytic temperature window and good reactivity, simultaneously preparation process is simple, raw material is easy to get, it is the catalyst of a kind of New high-efficient low-cost, it is adaptable to industry and the catalytic eliminating of the volatile organic contaminant such as aromatics, ketone, aldehydes in life.
A kind of be carrier with carbon titanium composite nano fiber loaded catalyst, the carbon titanium composite nano fiber that described catalyst is prepared with electrostatic spinning technique is for carrier, and with transition metal oxide for active component, wherein, the load capacity of described active component is 0~50%.
As preferably, described transition metal oxide is V2O5、Co3O4、MnO2、Cr2O3In the combination in any of one or two or more kinds.
As preferably, described carbon titanium composite nano fiber diameter is 100~500nm.
As preferably, described active component particles diameter is 2~100nm.
As preferably, the specific surface area of described catalyst is 50~200m2/g。
The preparation method of a kind of loaded catalyst being carrier with carbon titanium composite nano fiber, comprises the following steps:
(1) preparation solution
Taking polyvinylpyrrolidone and add in dehydrated alcohol as carbon precursor, stirring, to being completely dissolved, adds titanium precursors, active component presoma and hydrolysis inhibitor, and under room temperature, stirring obtains the precursor solution of spinning;
(2) electrostatic spinning
Precursor solution is irrigated jet by syringe, solution jet is stretched by high voltage electric field effect, is solidified, and to be wrapped in the accepter as fiber of the aluminium foil on cylinder, obtains the nanofiber of presoma component;
(3) calcining
In a nitrogen atmosphere, the nanofiber obtained after spinning is carried out high-temperature calcination, naturally cool to room temperature subsequently, finally give the catalyst of the carbon metal oxide-loaded active component of titanium composite nano fiber.
As preferably, the molal weight of described polyvinylpyrrolidone is 45000~55000g/mol.
As preferably, described titanium precursors is the combination in any of one or two or more kinds in butyl titanate, isopropyl titanate, titanium tetrachloride, titanium sulfate, titanyl sulfate;Described hydrolysis inhibitor is the combination in any of one or two or more kinds in glacial acetic acid, hydrochloric acid, triethanolamine, acrylic acid, neck Benzodiazepines, acetoacetic acid allyl ester, acetylacetone,2,4-pentanedione, sulphuric acid, nitric acid, phosphoric acid.
As preferably, in the preparation process of catalyst, the electrostatic potential that electrostatic spinning applies is 5~30kV, and receiving range is 10~25cm, and drum rotation speed is 50~100r/min, and syringe rate of flooding is 0.5~3mL/min;In calcination process, heating rate is 1~10 DEG C/min, and calcining heat is 400~500 DEG C.
The application of a kind of loaded catalyst being carrier with carbon titanium composite nano fiber, described catalyst is for aromatics, ketone, aldehydes volatile organic contaminant catalytic oxidative desulfurization in industrial tail gas and life.
The advantages such as the catalyst of the present invention has that preparation technology is simple, raw material is easy to get, removal efficiency height, long service life, the suitability are wide, it is adaptable to industrial tail gas and the volatile organic contaminant catalytic oxidative desulfurization such as aromatics, ketone, aldehydes in living.The present invention, with carbon titanium composite nano fiber for carrier, combines carbon carrier specific surface area is big, low temperature active is good advantage and TiO2The advantage that support is stable, sour site is many, has wider catalytic temperature window and good reactivity, has opened up the preparation method and application field of new catalytic filtering material, have stronger economy and good application prospect.
Accompanying drawing explanation
Fig. 1 is the XRD diffraction pattern of the nano-fiber catalyst obtained in embodiment 1;
Fig. 2 is the XRD diffraction pattern of the nano-fiber catalyst obtained in embodiment 2;
Fig. 3 is the XRD diffraction pattern of the nano-fiber catalyst obtained in embodiment 3;
Fig. 4 is the XRD diffraction pattern of the nano-fiber catalyst obtained in embodiment 4;
Fig. 5 is the scanning electron microscope image of the nano-fiber catalyst obtained in embodiment 3;
Fig. 6 is the curve that the conversion ratio of acetone catalytic oxidation is varied with temperature by the nano-fiber catalyst obtained in the embodiment of the present invention 1~4.
Detailed description of the invention
Below in conjunction with the drawings and specific embodiments, the invention will be further described, but invention which is intended to be protected is not limited to this.The technology related in embodiment, unless stated otherwise, is routine operation known in the art;The reagent that used, instrument, unless stated otherwise, all can be obtained by public approach.
Embodiment 1
A kind of be carrier with carbon titanium composite nano fiber loaded catalyst, the carbon titanium composite nano fiber that described catalyst is prepared with electrostatic spinning technique is for carrier, and with transition metal oxide for active component, wherein, the load capacity of described active component is 0%.
Described carbon titanium composite nano fiber diameter is 150nm, and the specific surface area of described catalyst is 122.6m2/g。
The preparation method of the above-mentioned loaded catalyst being carrier with carbon titanium composite nano fiber, specifically includes following steps:
(1) preparation solution
Take 1.5g polyvinylpyrrolidone (PVP, molal weight is 55000g/mol) as carbon precursor, add in 15mL dehydrated alcohol, magnetic agitation 30min to PVP is completely dissolved, add 3mL butyl titanate and 3mL glacial acetic acid, being made into the solution of V/Ti=0%, under room temperature, magnetic agitation 18h obtains precursor solution;
(2) electrostatic spinning
Plastic injector takes 9mL precursor solution, is fixed on the position of distance centre of the drum 15cm, and cylinder wraps up the aluminium foil reception device as nanofiber;Add high pressure power supply 15kV, drum rotation speed 50r/min at syringe rustless steel syringe needle place, and syringe rate of flooding is 1mL/min;Solution jet is stretched by high voltage electric field effect, solidifies, obtain the nanofiber of presoma component.
(3) calcining
After spinning terminates, take off aluminium foil in room temperature environment, place 12h, make nanofiber be fully hydrolyzed;Aluminium foil after placing is contained in crucible, puts into tube furnace and calcine in a nitrogen atmosphere, make fibers carbonization and remove organic component;Programming rate with 1 DEG C/min, it is heated to 200 DEG C from room temperature and keeps 1h, it is warming up to 500 DEG C with the speed of 1 DEG C/min again and keeps 1h, naturally cooling to room temperature, finally giving the catalyst (C-TiO of the carbon metal oxide-loaded active component of titanium composite nano fiber2Nano-fiber catalyst).
The XRD diffraction pattern of the nano-fiber catalyst that said method prepares is as shown in Figure 1.
Embodiment 2
A kind of be carrier with carbon titanium composite nano fiber loaded catalyst, the carbon titanium composite nano fiber that described catalyst is prepared with electrostatic spinning technique is for carrier, with transition metal oxide for active component, wherein, the load capacity of described active component is 10%, and described transition metal oxide is V2O5
Described carbon titanium composite nano fiber diameter is 187nm, and described active component particles diameter is 5.8nm, and the specific surface area of described catalyst is 83.2m2/g。
The preparation method of the above-mentioned loaded catalyst being carrier with carbon titanium composite nano fiber, specifically includes following steps:
(1) preparation solution
Take 1.5g polyvinylpyrrolidone (PVP, molal weight is 55000g/mol) as carbon precursor, add in 15mL dehydrated alcohol, magnetic agitation 30min to PVP is completely dissolved, add 3mL butyl titanate, 0.213g vanadyl acetylacetonate and 3mL glacial acetic acid, being made into the solution of V/Ti=10%, under room temperature, magnetic agitation 18h obtains precursor solution;
(2) electrostatic spinning
Plastic injector takes 9mL precursor solution, is fixed on the position of distance centre of the drum 15cm, and cylinder wraps up the aluminium foil reception device as nanofiber;Add high pressure power supply 15kV, drum rotation speed 50r/min at rustless steel syringe needle place, and syringe rate of flooding is 1mL/min;Solution jet is stretched by high voltage electric field effect, solidifies, obtain the nanofiber of presoma component;
(3) calcining
After spinning terminates, take off aluminium foil in room temperature environment, place 12h, make nanofiber be fully hydrolyzed;Aluminium foil after placing is contained in crucible, puts into tube furnace and calcine in a nitrogen atmosphere, make fibers carbonization and remove organic component;With the programming rate of 1 DEG C/min, it is heated to 200 DEG C from room temperature and keeps 1h, then be warming up to 500 DEG C with the speed of 1 DEG C/min and keep 1h, naturally cool to room temperature, finally give the V/C-TiO of V/Ti=10%2Nano-fiber catalyst.
The XRD diffraction pattern of the nano-fiber catalyst that said method prepares is as shown in Figure 2.
Embodiment 3
A kind of be carrier with carbon titanium composite nano fiber loaded catalyst, the carbon titanium composite nano fiber that described catalyst is prepared with electrostatic spinning technique is for carrier, with transition metal oxide for active component, wherein, the load capacity of described active component is 20%, and described transition metal oxide is V2O5
Described carbon titanium composite nano fiber diameter is 192nm, and described active component particles diameter is 6.7nm, and the specific surface area of described catalyst is 68.8m2/g。
The preparation method of the above-mentioned loaded catalyst being carrier with carbon titanium composite nano fiber, specifically includes following steps:
(1) preparation solution
Take 1.5g polyvinylpyrrolidone (PVP, molal weight is 55000g/mol) as carbon precursor, add in 15mL dehydrated alcohol, magnetic agitation 30min to PVP is completely dissolved, add 3mL butyl titanate, 0.425g vanadyl acetylacetonate and 3mL glacial acetic acid, being made into the solution of V/Ti=20%, under room temperature, magnetic agitation 18h obtains precursor solution;
(2) electrostatic spinning
Plastic injector takes 9mL precursor solution, is fixed on the position of distance centre of the drum 15cm, and cylinder wraps up the aluminium foil reception device as nanofiber;Add high pressure power supply 15kV, drum rotation speed 50r/min at rustless steel syringe needle place, and syringe rate of flooding is 1mL/min;Solution jet is stretched by high voltage electric field effect, solidifies, obtain the nanofiber of presoma component;
(3) calcining
After spinning terminates, take off aluminium foil in room temperature environment, place 12h, make nanofiber be fully hydrolyzed.Aluminium foil after placing is contained in crucible, puts into tube furnace and calcine in a nitrogen atmosphere, make fibers carbonization and remove organic component;With the programming rate of 1 DEG C/min, it is heated to 200 DEG C from room temperature and keeps 1h, then be warming up to 500 DEG C with the speed of 1 DEG C/min and keep 1h, naturally cool to room temperature, finally give the V/C-TiO of V/Ti=20%2Nano-fiber catalyst.
The XRD diffraction pattern of the nano-fiber catalyst that said method prepares as it is shown on figure 3, scanning electron microscope image as shown in Figure 5.
Embodiment 4
A kind of be carrier with carbon titanium composite nano fiber loaded catalyst, the carbon titanium composite nano fiber that described catalyst is prepared with electrostatic spinning technique is for carrier, with transition metal oxide for active component, wherein, the load capacity of described active component is 50%, and described transition metal oxide is V2O5
Described carbon titanium composite nano fiber diameter is 198nm, and described active component particles diameter is 7.8nm, and the specific surface area of described catalyst is 53.7m2/g。
The preparation method of the above-mentioned loaded catalyst being carrier with carbon titanium composite nano fiber, specifically includes following steps:
(1) preparation solution
Take 1.5g polyvinylpyrrolidone (PVP, molal weight is 55000g/mol) as carbon precursor, add in 15mL dehydrated alcohol, magnetic agitation 30min to PVP is completely dissolved, add 3mL butyl titanate, 1.062g vanadyl acetylacetonate and 3mL glacial acetic acid, being made into the solution of V/Ti=50%, under room temperature, magnetic agitation 18h obtains precursor solution;
(2) electrostatic spinning
Plastic injector takes 9mL precursor solution, is fixed on the position of distance centre of the drum 15cm, and cylinder wraps up the aluminium foil reception device as nanofiber;Add high pressure power supply 15kV, drum rotation speed 50r/min at rustless steel syringe needle place, and syringe rate of flooding is 1mL/min;Solution jet is stretched by high voltage electric field effect, solidifies, obtain the nanofiber of presoma component;
(3) calcining
After spinning terminates, take off aluminium foil in room temperature environment, place 12h, make nanofiber be fully hydrolyzed;Aluminium foil after placing is contained in crucible, puts into tube furnace and calcine in a nitrogen atmosphere, make fibers carbonization and remove organic component;With the programming rate of 1 DEG C/min, it is heated to 200 DEG C from room temperature and keeps 1h, then be warming up to 500 DEG C with the speed of 1 DEG C/min and keep 1h, naturally cool to room temperature, finally give the V/C-TiO of V/Ti=50%2Nano-fiber catalyst.
The XRD diffraction pattern of the nano-fiber catalyst that said method prepares is as shown in Figure 4.
Catalytic performance is tested
Grinding is sieved, and the granule taking 40~60 order sizes carries out catalytic eliminating performance test in VOCs removal efficiency experimental apparatus for testing.
The nano-fiber catalyst taking 45mg is placed on the central authorities of reactor, and unstrpped gas general gas flow is 60ml/min, and corresponding gas hourly space velocity (GHSV) is 20000h-1, unstrpped gas comprises 500ppm acetone and 5%O2, N2As Balance Air.
In order to ensure the safety and reliability of experiment, blank experiment is with rubble sand (40~60 order), in identical unstripped gas condition, and less than the 300 DEG C thermal decompositions not finding acetone.
The temperature E type thermocouple of catalytic bed and tubular heater is measured automatically, and the acetone concentration of entrance and exit measures with on-line gas chromatography (Agilent789A, USA) and flame ionization ditector (FID) at 60 DEG C.The computing formula of acetone removal efficiency is as follows:
η ( % ) = c i n - c o u t c i n × 100 %
In formula: η acetone conversion
cin,coutThe concentration of import and export place acetone
Each embodiment with carbon titanium composite nano fiber be carrier loaded catalyst (nano-fiber catalyst) when 300 DEG C the removal efficiency result of acetone is as shown in table 1:
Table 1
Nano-fiber catalyst Acetone removal efficiency
Embodiment 1 90%
Embodiment 2 96%
Embodiment 3 100%
Embodiment 4 87%
The curve that the conversion ratio of acetone catalytic oxidation is varied with temperature by the nano-fiber catalyst obtained in embodiment 1~4 is as shown in Figure 6.
From test result it can be seen that the nano-fiber catalyst of embodiment 3 shows higher reactivity, at acetone concentration 500ppm, air speed 20000h-1When, removal efficiency when 300 DEG C can reach 100%, and the removal efficiency of the nano-fiber catalyst of embodiment 4 is only 87%.This is due to the V/C-TiO in embodiment 32Nano-fiber catalyst has higher active component content and bigger specific surface area, catalytic oxidation can promote to the mass transport process such as reactant and the diffusion of product, Adsorption and desorption be attached, concurrently facilitate the active component avtive spot in the high degree of dispersion of catalyst surface, increase reaction, thus there is good catalytic reaction activity.
Above-described embodiment is only the preferred embodiment of the present invention, its object is to be more fully understood that the technology design of the present invention and feature, can not limit the scope of the invention with this.Described embodiment can be made amendment or supplements or adopt equivalent way to substitute by the research worker of art, without departing from the range of definition of the present invention.

Claims (10)

1. the loaded catalyst that a kind is carrier with carbon titanium composite nano fiber, it is characterized in that: the carbon titanium composite nano fiber that described catalyst is prepared with electrostatic spinning technique is for carrier, with transition metal oxide for active component, wherein, the load capacity of described active component is 0~50%.
2. according to claim 1 be carrier with carbon titanium composite nano fiber loaded catalyst, it is characterised in that: described transition metal oxide is V2O5、Co3O4、MnO2、Cr2O3In the combination in any of one or two or more kinds.
3. according to claim 1 be carrier with carbon titanium composite nano fiber loaded catalyst, it is characterised in that: described carbon titanium composite nano fiber diameter is 100~500nm.
4. according to claim 1 be carrier with carbon titanium composite nano fiber loaded catalyst, it is characterised in that: described active component particles diameter is 2~100nm.
5. according to claim 1 be carrier with carbon titanium composite nano fiber loaded catalyst, it is characterised in that: the specific surface area of described catalyst is 50~200m2/g。
6. the preparation method of catalyst described in a claim 1, it is characterised in that comprise the following steps:
(1) preparation solution
Taking polyvinylpyrrolidone and add in dehydrated alcohol as carbon precursor, stirring, to being completely dissolved, adds titanium precursors, active component presoma and hydrolysis inhibitor, and under room temperature, stirring obtains the precursor solution of spinning;
(2) electrostatic spinning
Precursor solution is irrigated jet by syringe, solution jet is stretched by high voltage electric field effect, is solidified, and to be wrapped in the reception device as fiber of the aluminium foil on cylinder, obtains the nanofiber of presoma component;
(3) calcining
In a nitrogen atmosphere, the nanofiber obtained after spinning is carried out high-temperature calcination, naturally cool to room temperature subsequently, finally give the catalyst of the carbon metal oxide-loaded active component of titanium composite nano fiber.
7. the preparation method of catalyst according to claim 6, it is characterised in that: the molal weight of described polyvinylpyrrolidone is 45000~55000g/mol.
8. the preparation method of catalyst according to claim 6, it is characterised in that: described titanium precursors is the combination in any of one or two or more kinds in butyl titanate, isopropyl titanate, titanium tetrachloride, titanium sulfate, titanyl sulfate;Described hydrolysis inhibitor is the combination in any of one or two or more kinds in glacial acetic acid, hydrochloric acid, triethanolamine, acrylic acid, neck Benzodiazepines, acetoacetic acid allyl ester, acetylacetone,2,4-pentanedione, sulphuric acid, nitric acid, phosphoric acid.
9. the preparation method of catalyst according to claim 6, it is characterized in that: in the preparation process of catalyst, the electrostatic potential that electrostatic spinning applies is 5~30kV, and receiving range is 10~25cm, drum rotation speed is 50~100r/min, and syringe rate of flooding is 0.5~3mL/min;In calcination process, heating rate is 1~10 DEG C/min, and calcining heat is 400~500 DEG C.
10. the application of the catalyst described in a claim 1, it is characterised in that: described catalyst is for aromatics, ketone, aldehydes volatile organic contaminant catalytic oxidative desulfurization in industrial tail gas and life.
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Cited By (6)

* Cited by examiner, † Cited by third party
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CN106955591A (en) * 2017-04-27 2017-07-18 北京达盛环保工程有限公司 The microwave catalysis of a kind of catalytic plate and the use catalytic plate cracks the device of bioxin
CN107119189A (en) * 2017-07-11 2017-09-01 攀钢集团研究院有限公司 A kind of precipitation method of the high sodium solution of the high chromium of high vanadium
CN108448126A (en) * 2018-02-09 2018-08-24 中南大学 A kind of PtAuTi nanowire catalytics material and preparation method thereof and application as fuel-cell catalyst
CN111804151A (en) * 2020-07-27 2020-10-23 上海恩捷新材料科技有限公司 MBR (membrane bioreactor) flat filter membrane for domestic sewage treatment and preparation method thereof
CN109775757B (en) * 2019-03-19 2021-09-28 广州大学 Preparation method of three-dimensional titanium dioxide material
CN115159606A (en) * 2022-08-10 2022-10-11 浙江大学 Method for treating organic sewage by utilizing solar energy photo-thermal catalysis

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20100031617A1 (en) * 2006-11-13 2010-02-11 Research Triangle Insitute Particle filter system incorporating nanofibers
CN104069851A (en) * 2014-06-16 2014-10-01 浙江大学 Metal oxide nano fiber for VOCs catalytic oxidation and preparation method thereof

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20100031617A1 (en) * 2006-11-13 2010-02-11 Research Triangle Insitute Particle filter system incorporating nanofibers
CN104069851A (en) * 2014-06-16 2014-10-01 浙江大学 Metal oxide nano fiber for VOCs catalytic oxidation and preparation method thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
宋春雨等: "静电纺丝法制备碳掺杂TiO2纳米纤维及其光降解性能研究", 《化工新型材料》 *

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106955591A (en) * 2017-04-27 2017-07-18 北京达盛环保工程有限公司 The microwave catalysis of a kind of catalytic plate and the use catalytic plate cracks the device of bioxin
CN106955591B (en) * 2017-04-27 2023-07-21 北京达盛环保工程有限公司 Catalytic plate and device for microwave catalytic cracking of dioxin by using same
CN107119189A (en) * 2017-07-11 2017-09-01 攀钢集团研究院有限公司 A kind of precipitation method of the high sodium solution of the high chromium of high vanadium
CN107119189B (en) * 2017-07-11 2018-11-20 攀钢集团研究院有限公司 A kind of precipitation method of the high sodium solution of the high chromium of high vanadium
CN108448126A (en) * 2018-02-09 2018-08-24 中南大学 A kind of PtAuTi nanowire catalytics material and preparation method thereof and application as fuel-cell catalyst
CN108448126B (en) * 2018-02-09 2020-09-04 中南大学 PtAuTi nanowire catalytic material, preparation method thereof and application of PtAuTi nanowire catalytic material as fuel cell catalyst
CN109775757B (en) * 2019-03-19 2021-09-28 广州大学 Preparation method of three-dimensional titanium dioxide material
CN111804151A (en) * 2020-07-27 2020-10-23 上海恩捷新材料科技有限公司 MBR (membrane bioreactor) flat filter membrane for domestic sewage treatment and preparation method thereof
CN115159606A (en) * 2022-08-10 2022-10-11 浙江大学 Method for treating organic sewage by utilizing solar energy photo-thermal catalysis
CN115159606B (en) * 2022-08-10 2024-01-26 浙江大学 Method for treating organic sewage by utilizing solar photo-thermal catalysis

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