CN108906017A - The preparation method of catalysis material for air cleaning - Google Patents

The preparation method of catalysis material for air cleaning Download PDF

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Publication number
CN108906017A
CN108906017A CN201810681422.8A CN201810681422A CN108906017A CN 108906017 A CN108906017 A CN 108906017A CN 201810681422 A CN201810681422 A CN 201810681422A CN 108906017 A CN108906017 A CN 108906017A
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titanium dioxide
obtains
30min
weight
air cleaning
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CN201810681422.8A
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高坤
张瑞锋
刘伟
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Jiangsu Environmental Protection Science And Technology Co Ltd
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Jiangsu Environmental Protection Science And Technology Co Ltd
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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
    • B01D53/007Separation 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 by irradiation
    • 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
    • B01J35/39
    • B01J35/58
    • 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
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0201Impregnation
    • 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
    • B01J37/08Heat treatment
    • B01J37/10Heat treatment in the presence of water, e.g. steam
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/70Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
    • B01D2257/704Solvents not covered by groups B01D2257/702 - B01D2257/7027
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/06Polluted air
    • 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • 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

Abstract

This application discloses a kind of preparation methods of catalysis material for air cleaning, including:(1), modifying titanium dioxide is prepared;(3), using modificationization titanium as raw material, mass concentration is prepared in 6%~8% titanium dioxide composite photocatalyst suspension;(4), hollow carbon fiber carrier is prepared;(5), by hollow carbon fiber carrier impregnation in titanium dioxide composite photocatalyst suspension 20~40min, lifting come out after in 90~110 DEG C of dry 90~120min;Continue the 10~30min in titanium dioxide composite photocatalyst suspension of the hollow carbon fiber carrier impregnation after drying, in 90~120 DEG C of dry 50~100min after lifting out, obtains the catalysis material for being used for air cleaning.Its Formaldehyde decomposition speed of material of the invention is fast, and degradation rate is high, and formaldehyde gas degradation rate can reach 95.3%, and photocatalytic water hydrogen-producing speed is up to 43.5mmol/h/g.

Description

The preparation method of catalysis material for air cleaning
Technical field
This application involves technical field of air purification, more particularly to a kind of system of catalysis material for air cleaning Preparation Method.
Background technique
Studies have shown that photocatalysis technology has good application prospect photochemical catalyst that can divide in terms of environmental pollution improvement It dissipates and light catalyzed coating is made in resin, can not only make coating that there is excellent performance, can also be effectively reduced in environment dirty The concentration of metachromia gas makes organic or inorganic pollutant that redox reaction occur under photocatalysis, generates H2O、CO2And The substances such as salt reach innoxious, thus environment purification.
Titanium dioxide (TiO2), photon can be captured and realize separation of charge, be most common catalysis material.Such nothing The photocatalytic process of machine semiconductor light-catalyst be by light excitation generate electrons and holes, respectively be adsorbed onto catalyst The species on surface occur reduction and oxidation reaction and realize.But its photochemical catalyst powder faces photocatalysis in application process The problems such as low efficiency and low adsorbance.
Summary of the invention
It is existing to overcome the purpose of the present invention is to provide a kind of preparation method of catalysis material for air cleaning Deficiency in technology.
To achieve the above object, the present invention provides the following technical solutions:
The embodiment of the present application discloses a kind of preparation method of catalysis material for air cleaning, including:
(1), by titania powder and phenol according to 1:0.8~2 weight ratio is blended in potassium hydroxide solution, and magnetic force stirs Mix and carry out hydro-thermal reaction after 10~30min, 120~180 DEG C of reaction temperature, the reaction time 20~70 hours, potassium hydroxide it is dense Degree is 4~8mol/L;
(2), reaction product and benzyl carbinol are according to 1:0.8~2 weight ratio be added in nitric acid solution be mixed 10~ The concentration of 30min, nitric acid solution are 0.3~0.7mol/L, then solid matter with deionized water is washed to neutrality, then 60 Dry 10~30min, is finally heat-treated 4~10 hours under 700~1000 DEG C of high temperature under the conditions of~100 DEG C, obtains modified two Titanium oxide;
(3), using modificationization titanium as raw material, preparation mass concentration suspends in 6%~8% titanium dioxide composite photocatalyst Liquid;
(4), hollow carbon fiber carrier is prepared;
(5), 20~40min, lifting in titanium dioxide composite photocatalyst suspension by hollow carbon fiber carrier impregnation In 90~110 DEG C of dry 90~120min after out;Continue the hollow carbon fiber carrier impregnation after drying to answer in titanium dioxide 10~30min in light combination catalyst suspension is obtained in 90~120 DEG C of dry 50~100min after lifting out and is used for air The catalysis material of purification.
Preferably, in the preparation method of the above-mentioned catalysis material for air cleaning, step (3) includes:
Under normal temperature conditions, by the sodium hydrogen telluride of 50~70 parts by weight, the modifying titanium dioxide of 1500~1800 parts by weight It is add to deionized water, 10~30min of magnetic agitation, obtains the first mixed solution;
Under normal temperature conditions, by the mercaptopropionic acid of the cadmium acetate of 50~70 parts by weight, 50~80 parts by weight be added to from 10~30min of ultrasonic disperse in sub- water obtains the second mixed solution;
Second mixed solution is added into the first mixed solution, is heated to 70~100 DEG C, 20~60min is mixed, Obtain titanium dioxide composite photocatalyst suspension.
Preferably, in the preparation method of the above-mentioned catalysis material for air cleaning, titanium dioxide complex light is urged Agent suspension concentration is 7.5%.
Preferably, in the preparation method of the above-mentioned catalysis material for air cleaning, step (4) includes:
Under 370~450 DEG C of hot conditions, spinning is carried out to polyacrylonitrile by spinning machine, obtains doughnut, then In chemical crosslinking device, oxygen, which is added, makes it react 20~30min at 50~60 DEG C, washs to doughnut, removes Then the impurity on surface first impregnates 8~15min in an acidic solution, wash to neutrality, then proceed to impregnate in alkaline solution 10~20min is washed to neutrality, is then carbonized 1~3 hour in 2500~2800 DEG C of graphitizing furnace.
Disclosed herein as well is a kind of preparation methods of catalysis material for air cleaning, including:
By titania powder and phenol according to 1:1.5 weight ratios are blended in potassium hydroxide solution, magnetic agitation 10min After carry out hydro-thermal reaction, 160 DEG C of reaction temperature, the reaction time 36 hours, the concentration of potassium hydroxide was 5mol/L, reaction product and Benzyl carbinol is according to 1:1.5 weight ratios, which are added in nitric acid solution, is mixed 30min, and the concentration of nitric acid solution is 0.3mol/L, Solid matter with deionized water is washed to neutrality again, 20min is then dried under the conditions of 80 DEG C, finally under 800 DEG C of high temperature Heat treatment 6 hours obtains modifying titanium dioxide;
Under normal temperature conditions, by the modifying titanium dioxide of the sodium hydrogen telluride of 50 parts by weight, 1700 parts by weight be added to from In sub- water, magnetic agitation 20min obtains the first mixed solution;
Under normal temperature conditions, the mercaptopropionic acid of the cadmium acetate of 60 parts by weight, 70 parts by weight is add to deionized water super Sound disperses 10min, obtains the second mixed solution;
Second mixed solution is added into the first mixed solution, is heated to 80 DEG C, 20min is mixed, obtains quality Concentration is in 7.5% titanium dioxide composite photocatalyst suspension;
Under 400 DEG C of hot conditions, spinning is carried out to polyacrylonitrile by spinning machine, doughnut is obtained, is then changing It learns in crosslinking device, oxygen, which is added, makes it react 30min at 60 DEG C, washs to doughnut, removes the impurity on surface, so First impregnate 10min in an acidic solution afterwards, washing to neutrality then proceedes to impregnate 10min in alkaline solution, washs into Property, it is then carbonized 2 hours in 2600 DEG C of graphitizing furnace, obtains hollow carbon fiber carrier;
By hollow carbon fiber carrier impregnation in titanium dioxide composite photocatalyst suspension 40min, lifting come out after 110 DEG C of dry 120min;Continue the hollow carbon fiber carrier impregnation after drying in titanium dioxide composite photocatalyst suspension Middle 10min obtains the catalysis material for being used for air cleaning in 110 DEG C of dry 70min after lifting out.With prior art phase Than, the advantage of the invention is that:Its Formaldehyde decomposition speed of material of the invention is fast, and degradation rate is high, and formaldehyde gas degradation rate can Reach 95.3%, photocatalytic water hydrogen-producing speed is up to 43.5mmol/h/g.
Specific embodiment
The present invention is described further by the following example:According to following embodiments, the present invention may be better understood. However, as it will be easily appreciated by one skilled in the art that specific material ratio, process conditions and its result described in embodiment are only used In illustrating the present invention, without the present invention described in detail in claims should will not be limited.
Embodiment 1
By titania powder and phenol according to 1:1.5 weight ratios are blended in potassium hydroxide solution, magnetic agitation 10min After carry out hydro-thermal reaction, 160 DEG C of reaction temperature, the reaction time 36 hours, the concentration of potassium hydroxide was 5mol/L.Reaction product and Benzyl carbinol is according to 1:1.5 weight ratios, which are added in nitric acid solution, is mixed 30min, and the concentration of nitric acid solution is 0.3mol/L. Solid matter with deionized water is washed to neutrality again, 20min is then dried under the conditions of 80 DEG C.Finally under 800 DEG C of high temperature Heat treatment 6 hours obtains modifying titanium dioxide.
Under normal temperature conditions, the modifying titanium dioxide of the sodium hydrogen telluride of 50mg, 1700mg are add to deionized water, magnetic Power stirs 20min, obtains the first mixed solution;
Under normal temperature conditions, the mercaptopropionic acid of the cadmium acetate of 60mg, 70mg are add to deionized water ultrasonic disperse 10min obtains the second mixed solution.
Second mixed solution is slowly added into the first mixed solution, is heated to 80 DEG C, 20min is mixed, is obtained Mass concentration is in 7.5% titanium dioxide composite photocatalyst suspension.
Under 400 DEG C of hot conditions, spinning is carried out to polyacrylonitrile by spinning machine, doughnut is obtained, is then changing It learns in crosslinking device, oxygen, which is added, makes it react 30min at 60 DEG C.Doughnut is washed, removes the impurity on surface, so First impregnate 10min in an acidic solution afterwards, washing to neutrality then proceedes to impregnate 10min in alkaline solution, washs into Property, it is then carbonized 2 hours in 2600 DEG C of graphitizing furnace, obtains hollow carbon fiber carrier.
By hollow carbon fiber carrier impregnation in titanium dioxide composite photocatalyst suspension 40min, lifting come out after 110 DEG C of dry 120min;Continue the hollow carbon fiber carrier impregnation after drying in titanium dioxide composite photocatalyst suspension Middle 10min obtains composite photocatalyst material in 110 DEG C of dry 70min after lifting out.
Degradation test is carried out in closed space PARA FORMALDEHYDE PRILLS(91,95), controls 22 DEG C of environment temperature, gas flow rate 1.5m/s, environment phase To humidity 45%, initial concentration of formaldehyde 5mg/m3.It can be found that:
Concentration of formaldehyde is stablized after 55min, and formaldehyde gas degradation rate reaches 95.3%.
Moreover, photocatalytic water hydrogen-producing speed is up under the AM 1.5G simulated solar irradiation irradiation of 1 sun intensity 43.5mmol/h/g。
Comparative example 1
Under normal temperature conditions, the commercially available titanium dioxide of 200mg is add to deionized water, magnetic agitation 20min;It obtains Mass concentration is in 7.5% titanium dioxide optical catalyst suspension.
Under 400 DEG C of hot conditions, spinning is carried out to polyacrylonitrile by spinning machine, doughnut is obtained, is then changing It learns in crosslinking device, oxygen, which is added, makes it react 30min at 60 DEG C.Doughnut is washed, removes the impurity on surface, so First impregnate 10min in an acidic solution afterwards, washing to neutrality then proceedes to impregnate 10min in alkaline solution, washs into Property, it is then carbonized 2 hours in 2600 DEG C of graphitizing furnace, obtains hollow carbon fiber carrier.
By hollow carbon fiber carrier impregnation in titanium dioxide composite photocatalyst suspension 40min, lifting come out after 110 DEG C of dry 120min;Continue the hollow carbon fiber carrier impregnation after drying in titanium dioxide composite photocatalyst suspension Middle 10min obtains composite photocatalyst material in 110 DEG C of dry 70min after lifting out.
Degradation test is carried out in closed space PARA FORMALDEHYDE PRILLS(91,95), controls 22 DEG C of environment temperature, gas flow rate 1.5m/s, environment phase To humidity 45%, initial concentration of formaldehyde 5mg/m3.It can be found that:
Concentration of formaldehyde is stablized after 100min, and formaldehyde gas degradation rate reaches 85.1%.
Under the AM 1.5G simulated solar irradiation irradiation of 1 sun intensity, photocatalytic water hydrogen-producing speed is 8.1mmol/h/g.
Comparative example 2
By titania powder and phenol according to 1:1.5 weight ratios are blended in potassium hydroxide solution, magnetic agitation 10min After carry out hydro-thermal reaction, 160 DEG C of reaction temperature, the reaction time 36 hours, the concentration of potassium hydroxide was 5mol/L.Reaction product and Benzyl carbinol is according to 1:1.5 weight ratios, which are added in nitric acid solution, is mixed 30min, and the concentration of nitric acid solution is 0.3mol/L. Solid matter with deionized water is washed to neutrality again, 20min is then dried under the conditions of 80 DEG C.Finally under 800 DEG C of high temperature Heat treatment 6 hours obtains modifying titanium dioxide.
Under normal temperature conditions, the modifying titanium dioxide of the sodium hydrogen telluride of 50mg, 1700mg are add to deionized water, magnetic Power stirs 20min, obtains the first mixed solution;
Under normal temperature conditions, the mercaptopropionic acid of the cadmium acetate of 60mg, 70mg are add to deionized water ultrasonic disperse 10min obtains the second mixed solution.
Second mixed solution is slowly added into the first mixed solution, is heated to 80 DEG C, 20min is mixed, is obtained Mass concentration is in 7.5% titanium dioxide composite photocatalyst suspension.
Commercially available carbon fiber is provided as carrier (STF-1000T type, Jiangsu Sutong Carbon Fiber Co., Ltd).
By hollow carbon fiber carrier impregnation in titanium dioxide composite photocatalyst suspension 40min, lifting come out after 110 DEG C of dry 120min;Continue the hollow carbon fiber carrier impregnation after drying in titanium dioxide composite photocatalyst suspension Middle 10min obtains composite photocatalyst material in 110 DEG C of dry 70min after lifting out.
Degradation test is carried out in closed space PARA FORMALDEHYDE PRILLS(91,95), controls 22 DEG C of environment temperature, gas flow rate 1.5m/s, environment phase To humidity 45%, initial concentration of formaldehyde 5mg/m3.It can be found that:
Concentration of formaldehyde is stablized after 70min, and formaldehyde gas degradation rate reaches 92.3%.
Moreover, photocatalytic water hydrogen-producing speed is up under the AM 1.5G simulated solar irradiation irradiation of 1 sun intensity 38.3mmol/h/g。
It is compared with comparative example 1-2 it is found that the Degradation Formaldehyde effect and photocatalytic water hydrogen-producing speed of embodiment 1 are bright by embodiment 1 It is aobvious to be higher than documents 1 and documents 2.
Finally, it is to be noted that, the terms "include", "comprise" or its any other variant be intended to it is non-exclusive Property include so that include a series of elements process, method, article or equipment not only include those elements, but also Further include other elements that are not explicitly listed, or further include for this process, method, article or equipment it is intrinsic Element.

Claims (5)

1. a kind of preparation method of the catalysis material for air cleaning, which is characterized in that including:
(1), by titania powder and phenol according to 1:0.8~2 weight ratio is blended in potassium hydroxide solution, magnetic agitation 10 Hydro-thermal reaction is carried out after~30min, 120~180 DEG C of reaction temperature, the reaction time 20~70 hours, the concentration of potassium hydroxide was 4 ~8mol/L;
(2), reaction product and benzyl carbinol are according to 1:0.8~2 weight ratio is added to 10~30min of mixing in nitric acid solution, The concentration of nitric acid solution is 0.3~0.7mol/L, then solid matter with deionized water is washed to neutrality, then 60~100 Dry 10~30min, is finally heat-treated 4~10 hours under 700~1000 DEG C of high temperature under the conditions of DEG C, obtains modified titanium dioxide Titanium;
(3), using modificationization titanium as raw material, mass concentration is prepared in 6%~8% titanium dioxide composite photocatalyst suspension;
(4), hollow carbon fiber carrier is prepared;
(5), by hollow carbon fiber carrier impregnation, 20~40min, lifting are come out in titanium dioxide composite photocatalyst suspension Afterwards in 90~110 DEG C of dry 90~120min;Continue the hollow carbon fiber carrier impregnation after drying in titanium dioxide complex light 10~30min in catalyst suspension is obtained in 90~120 DEG C of dry 50~100min after lifting out and is used for air cleaning Catalysis material.
2. the preparation method of the catalysis material according to claim 1 for air cleaning, which is characterized in that step (3) include:
Under normal temperature conditions, the modifying titanium dioxide of the sodium hydrogen telluride of 50~70 parts by weight, 1500~1800 parts by weight is added Into deionized water, 10~30min of magnetic agitation obtains the first mixed solution;
Under normal temperature conditions, the mercaptopropionic acid of the cadmium acetate of 50~70 parts by weight, 50~80 parts by weight is added to deionized water Middle 10~30min of ultrasonic disperse obtains the second mixed solution;
Second mixed solution is added into the first mixed solution, is heated to 70~100 DEG C, 20~60min is mixed, is obtained Titanium dioxide composite photocatalyst suspension.
3. the preparation method of the catalysis material according to claim 1 for air cleaning, which is characterized in that titanium dioxide Titanium composite photo-catalyst suspension concentration is 7.5%.
4. the preparation method of the catalysis material according to claim 1 for air cleaning, which is characterized in that step (4) include:
Under 370~450 DEG C of hot conditions, spinning is carried out to polyacrylonitrile by spinning machine, doughnut is obtained, is then changing It learns in crosslinking device, oxygen, which is added, makes it react 20~30min at 50~60 DEG C, washs to doughnut, removes surface Impurity, then first impregnate 8~15min in an acidic solution, washing to neutrality, then proceed to impregnate 10 in alkaline solution~ 20min is washed to neutrality, is then carbonized 1~3 hour in 2500~2800 DEG C of graphitizing furnace.
5. a kind of preparation method of the catalysis material for air cleaning, which is characterized in that including:
By titania powder and phenol according to 1:1.5 weight ratios are blended in potassium hydroxide solution, and magnetic agitation 10min is laggard Row hydro-thermal reaction, 160 DEG C of reaction temperature, the reaction time 36 hours, the concentration of potassium hydroxide was 5mol/L, reaction product and benzene second Alcohol is according to 1:1.5 weight ratios, which are added in nitric acid solution, is mixed 30min, and the concentration of nitric acid solution is 0.3mol/L, then will Solid matter with deionized water is washed to neutrality, 20min is then dried under the conditions of 80 DEG C, finally under 800 DEG C of high temperature at heat Reason 6 hours obtains modifying titanium dioxide;
Under normal temperature conditions, the modifying titanium dioxide of the sodium hydrogen telluride of 50 parts by weight, 1700 parts by weight is added to deionized water In, magnetic agitation 20min obtains the first mixed solution;
Under normal temperature conditions, the mercaptopropionic acid of the cadmium acetate of 60 parts by weight, 70 parts by weight is add to deionized water ultrasound point 10min is dissipated, the second mixed solution is obtained;
Second mixed solution is added into the first mixed solution, is heated to 80 DEG C, 20min is mixed, obtains mass concentration In 7.5% titanium dioxide composite photocatalyst suspension;
Under 400 DEG C of hot conditions, spinning is carried out to polyacrylonitrile by spinning machine, obtains doughnut, is then handed in chemistry Join in device, oxygen, which is added, makes it react 30min at 60 DEG C, washs to doughnut, removes the impurity on surface, then first 10min is impregnated in an acidic solution, and washing to neutrality then proceedes to impregnate 10min in alkaline solution, washing to neutrality, so It is carbonized 2 hours in 2600 DEG C of graphitizing furnace afterwards, obtains hollow carbon fiber carrier;
By hollow carbon fiber carrier impregnation in titanium dioxide composite photocatalyst suspension 40min, lifting come out after at 110 DEG C Dry 120min;Continue the hollow carbon fiber carrier impregnation after drying in titanium dioxide composite photocatalyst suspension 10min obtains the catalysis material for being used for air cleaning in 110 DEG C of dry 70min after lifting out.
CN201810681422.8A 2018-06-27 2018-06-27 The preparation method of catalysis material for air cleaning Withdrawn CN108906017A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115212874A (en) * 2022-08-16 2022-10-21 深圳市康弘智能健康科技股份有限公司 Preparation method of improved photocatalytic material for catalytic purification of formaldehyde by visible light

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107973342A (en) * 2017-12-25 2018-05-01 湘潭大学 A kind of ultra-thin exposure of carbon coating (010) crystal face single crystal titanium dioxide nanobelt and preparation method thereof
CN108048957A (en) * 2017-12-26 2018-05-18 宜兴市天宇世纪高新科技有限公司 A kind of preparation process of the activated carbon fiber of hollow structure
CN108067267A (en) * 2017-12-19 2018-05-25 中国计量大学 A kind of visible light-responded cadmium telluride/titanium dioxide Z-type photochemical catalyst and its preparation method and application
CN108201789A (en) * 2017-12-19 2018-06-26 如皋六维环境科技有限公司 A kind of preparation method of purifying formaldehyde material and application

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108067267A (en) * 2017-12-19 2018-05-25 中国计量大学 A kind of visible light-responded cadmium telluride/titanium dioxide Z-type photochemical catalyst and its preparation method and application
CN108201789A (en) * 2017-12-19 2018-06-26 如皋六维环境科技有限公司 A kind of preparation method of purifying formaldehyde material and application
CN107973342A (en) * 2017-12-25 2018-05-01 湘潭大学 A kind of ultra-thin exposure of carbon coating (010) crystal face single crystal titanium dioxide nanobelt and preparation method thereof
CN108048957A (en) * 2017-12-26 2018-05-18 宜兴市天宇世纪高新科技有限公司 A kind of preparation process of the activated carbon fiber of hollow structure

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115212874A (en) * 2022-08-16 2022-10-21 深圳市康弘智能健康科技股份有限公司 Preparation method of improved photocatalytic material for catalytic purification of formaldehyde by visible light

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