CN106807398B - It is a kind of under water vapour environment eliminate carbon monoxide and the catalyst of formaldehyde and preparation method thereof - Google Patents
It is a kind of under water vapour environment eliminate carbon monoxide and the catalyst of formaldehyde and preparation method thereof Download PDFInfo
- Publication number
- CN106807398B CN106807398B CN201710006800.8A CN201710006800A CN106807398B CN 106807398 B CN106807398 B CN 106807398B CN 201710006800 A CN201710006800 A CN 201710006800A CN 106807398 B CN106807398 B CN 106807398B
- Authority
- CN
- China
- Prior art keywords
- catalyst
- composite oxide
- hours
- carrier
- oxide carrier
- 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.)
- Active
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/002—Mixed oxides other than spinels, e.g. perovskite
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/864—Removing carbon monoxide or hydrocarbons
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8668—Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/70—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
- B01J23/89—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
- B01J23/8933—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/898—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with vanadium, tantalum, niobium or polonium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/40—Nitrogen compounds
- B01D2257/404—Nitrogen oxides other than dinitrogen oxide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/70—Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2523/00—Constitutive chemical elements of heterogeneous catalysts
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Biomedical Technology (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Analytical Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Organic Chemistry (AREA)
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
It is a kind of under water vapour environment eliminate carbon monoxide and the catalyst of formaldehyde and preparation method thereof, with Ce0.8Fe0.1Co0.1VO4Composite oxides are carrier, Pt is that active component, In and K are co-catalyst composition;The quality of precious metals pt is Ce0.8Fe0.1Co0.1VO4The 1-3% of composite oxide carrier;The quality of co-catalyst In is Ce0.8Fe0.1Co0.1VO4The 0.05-0.3% of composite oxide carrier;The quality of co-catalyst K is Ce0.8Fe0.1Co0.1VO4The 0.01-0.1% of composite oxide carrier.The catalyst prepares Ce using sol-gal process0.8Fe0.1Co0.1VO4Composite oxide carrier, then by Pt (NO3)2、In(NO3)3, potassium citrate mixed solution, with infusion process prepare Ce0.8Fe0.1Co0.1VO4Supporting Pt, In, K catalyst.Activity and stability of the catalyst under water vapour environment can be significantly increased in the catalyst.
Description
Technical field
The present invention relates to a kind of chemical catalysts, in particular to a kind of for eliminating carbon monoxide and formaldehyde under water vapour environment
Catalyst and preparation method thereof.
Background technique
CO and formaldehyde are typical toxic and harmful gas, are most commonly seen one of gaseous pollutants.Carbon monoxide intrusion
Body will be combined into carbonyl haemoglobin with hemoglobin quickly, so that it is red to hinder oxygen with hemoglobin to be combined into oxygenated blood
Albumen.Poisoner just will appear weak pulse, and breathing is slack-off, and last failure is lethal.Formaldehyde is more highly toxic substance, toxic in China
Formaldehyde is in second on chemicals priority acccess control list.Concentration of formaldehyde reaches 0.06-0.07mg/m3 in every cubic metres of air
When, children will occur slightly to pant.When formaldehyde content in indoor air is 0.1mg/m3, just there are peculiar smell and sense of discomfort;It reaches
When to 0.5mg/m3, eyes can be stimulated, cause to shed tears;Reach 0.6mg/m3, throat discomfort or pain can be caused.Long Term Contact is low
Dosage formaldehyde can also cause chronic respiratory disease, and newly-decorated room content of formaldehyde is higher, be the main inducing of numerous diseases.
CO is eliminated by catalysis oxidation and formaldehyde is the common method of industry, since there are many elimination CO and formaldehyde under low temperature
Aspect all has a very high practical value, therefore researches and develops low temperature or eliminate CO at room temperature and the catalyst of formaldehyde is constantly subjected to science
The concern on boundary and industry.CO is eliminated, air cleaning, closed-circulation CO2 laser, CO gas sensing are mainly used for
CO elimination in device, the control of vehicle exhaust, CO breathing mask and closed system etc..And formaldehyde is eliminated, and is mainly used for
The indoor air cleaning of civil building engineering.Carbon monoxide and formaldehyde eliminate catalyst used mainly have noble metal catalyst and
Non-precious metal catalyst, noble metal is with its good CO, O2Absorption and activity function are considered as catalysis CO and the complete oxygen of formaldehyde
The preferred catalyst of change.Researcher is often through the preparation method for changing catalyst, regulating catalyst carrier and co-catalyst
To improve the performance of Pt catalyst, the stability used under the stability especially water vapour environment of effort raising catalyst.
Summary of the invention
It is an object of the invention to eliminate the problem of stability difference existing for catalyst for existing carbon monoxide and formaldehyde,
It provides a kind of for eliminating carbon monoxide and the high performance catalyst of formaldehyde and preparation method thereof under water vapour environment.
To solve this technical problem, the technical solution adopted by the present invention are as follows:
A kind of Pt-In-K/Ce for elimination carbon monoxide and formaldehyde under water vapour environment0.8Fe0.1Co0.1VO4Catalyst,
It is characterized by: the catalyst is with Ce0.8Fe0.1Co0.1VO4Composite oxides are carrier, Pt is that active component, In and K are to help to urge
Agent composition.Ce0.8Fe0.1Co0.1VO4In composite oxide carrier, the molar ratio of Ce, Fe, Co, V are 0.8:0.1:0.1:1;It is expensive
The quality of Pt metal is Ce0.8Fe0.1Co0.1VO4The 1-3% of composite oxide carrier;The quality of co-catalyst In is
Ce0.8Fe0.1Co0.1VO4The 0.05-0.3% of composite oxide carrier;The quality of co-catalyst K is Ce0.8Fe0.1Co0.1VO4It is compound
The 0.01-0.1% of oxide carrier.
The catalyst the preparation method comprises the following steps: using sol-gal process prepare Ce0.8Fe0.1Co0.1VO4Composite oxide carrier,
Then by Pt (NO3)2、In(NO3)3, potassium citrate mixed solution, with infusion process prepare Ce0.8Fe0.1Co0.1VO4Supporting Pt, In, K
Catalyst, i.e. Pt-In-K/Ce0.8Fe0.1Co0.1VO4Catalyst.
Specifically comprise the following steps:
(1) by Ce (NO3)3·6H2O、Fe(NO3)3·9H2O、Co(NO3)3·6H2O、VOC2O4·5H2O and citric acid are pressed
It is that 0.80:0.10:0.10:1.0:0.50 is dissolved in deionized water according to molar ratio, in 90 DEG C of stirring in water bath to gel after being completely dissolved
State, then 120 DEG C drying 8 hours, finally roast 4 hours under 500 DEG C of air atmospheres, obtain Ce0.8Fe0.1Co0.1VO4It carries
Body, citric acid resolves into carbon dioxide completely by roasting and water leaves catalyst.
(2) by Pt (NO3)2、In(NO3)3, potassium citrate mixed solution be added Ce0.8Fe0.1Co0.1VO4In carrier, dipping 2
Hour, then 90 DEG C of water-bath fried drys, 120 DEG C are dried 8 hours, are roasted 5 hours under last 350 DEG C of nitrogen atmospheres, are then switched to sky
300 DEG C of gas atmosphere roast 4 hours, obtain Pt-In-K/Ce0.8Fe0.1Co0.1VO4Catalyst.Wherein the quality of precious metals pt is
Ce0.8Fe0.1Co0.1VO4The 1-3% of composite oxide carrier;The quality of co-catalyst In is Ce0.8Fe0.1Co0.1VO4Combined oxidation
The 0.05-0.3% of object carrier;The quality of co-catalyst K is Ce0.8Fe0.1Co0.1VO4The 0.01- of composite oxide carrier
0.1%.
The catalyst prepared in aforementioned manners, by Ce0.8Fe0.1Co0.1VO4Composite oxide carrier and precious metals pt are
Active component, In and K are co-catalyst combination, and activity and stabilization of the catalyst under water vapour environment can be significantly increased
Property.
Specific embodiment
The present invention is made below with reference to embodiment and further being illustrated, but the present invention is not limited to these implementations
Example.
Embodiment 1
(1) by Ce (NO3)3·6H2O、Fe(NO3)3·9H2O、Co(NO3)3·6H2O、VOC2O4·5H2O and citric acid are pressed
It is 0.80:0.10:0.10:1.0:0.50 according to molar ratio, by 69.5 grams of Ce (NO3)3·6H2O, 8.08 grams of Fe (NO3)3·9H2O、
9.03 grams of Co (NO3)3·6H2O, 49.0 grams of VOC2O4·5H2O and 19.2 gram of citric acid is dissolved in deionized water, after being completely dissolved in
90 DEG C of stirring in water bath are to gel state, and then 120 DEG C drying 8 hours, finally roast 4 hours under 500 DEG C of air atmospheres, obtain
Ce0.8Fe0.1Co0.1VO4Carrier.
(2) according to Pt, In and K in Ce0.8Fe0.1Co0.1VO4Mass percentage in composite oxide carrier is respectively
1.0%, 0.20% and 0.05%.By the Pt (NO containing 1.0 grams of Pt3)2Solution, 0.68 gram of In (NO3)3·5H2O and 0.14 gram of lemon
Lemon acid potassium is diluted to 100ml with deionized water, is completely dissolved.It is then added to 100g Ce0.8Fe0.1Co0.1VO4Composite oxides
In carrier, impregnate 2 hours, then 90 DEG C of water-bath fried drys, 120 DEG C are dried 8 hours, then roasted 5 hours under 350 DEG C of nitrogen atmospheres,
It is finally switched to 300 DEG C of air atmosphere to roast 4 hours, obtains the Pt-In-K/Ce of embodiment 10.8Fe0.1Co0.1VO4Catalyst.
(3) the catalyst tabletting prepared is sieved by catalyst activity test condition, selects 100-120 purpose to urge later
Catalyst particles, dosage 0.1g are fitted into the quartz ampoule (internal diameter 6mm) for reaction.CO is aoxidized, reaction gas 1%
CO+1%O2+ 2%H2O, remaining is nitrogen, and wherein air speed is 60000mLg-1h-1, measure the CO reactivity worth of catalyst.It is right
In oxidation of formaldehyde, reaction gas is 0.1% formaldehyde+1%O2+ 2%H2O, remaining is nitrogen, and wherein air speed is 60000mLg-1h-1,
Measure the CO reactivity worth of catalyst.The CO oxidation susceptibility of catalyst indicates with conversion ratio under 70 DEG C of reaction conditions, respectively
The conversion ratio variation of measurement 1 hour and 10 hours, to investigate the stability of catalyst.The oxidation of formaldehyde performance of catalyst is with 60 DEG C
Conversion ratio under reaction condition indicates, measures 1 hour and 10 hours conversion ratio respectively and changes, to investigate the stabilization of catalyst
Property.The reactivity worth of catalyst is shown in Table 1.
Embodiment 2
(1)Ce0.8Fe0.1Co0.1VO4The preparation method of carrier is same as Example 1.
(2) according to Pt, In and K in Ce0.8Fe0.1Co0.1VO4Mass percentage in composite oxide carrier is respectively
2.0%, 0.20% and 0.05%.By the Pt (NO containing 2.0 grams of Pt3)2Solution, 0.68 gram of In (NO3)3·5H2O and 0.14 gram of lemon
Lemon acid potassium is diluted to 100ml with deionized water, is completely dissolved.It is then added to 00g Ce0.8Fe0.1Co0.1VO4Composite oxides
In carrier, impregnate 2 hours, then 90 DEG C of water-bath fried drys, 120 DEG C are dried 8 hours, then roasted 5 hours under 350 DEG C of nitrogen atmospheres,
It is finally switched to 300 DEG C of air atmosphere to roast 4 hours, obtains the Pt-In-K/Ce of embodiment 20.8Fe0.1Co0.1VO4Catalyst.
(3) catalyst activity test condition is same as Example 1.The reactivity worth of catalyst is shown in Table 1.
Embodiment 3
(1)Ce0.8Fe0.1Co0.1VO4The preparation method of carrier is same as Example 1.
(2) according to Pt, In and K in Ce0.8Fe0.1Co0.1VO4Mass percentage in composite oxide carrier is respectively
3.0%, 0.20% and 0.05%.By the Pt (NO containing 3.0 grams of Pt3)2Solution, 0.68 gram of In (NO3)3·5H2O and 0.14 gram of lemon
Lemon acid potassium is diluted to 100ml with deionized water, is completely dissolved.It is then added to 100g Ce0.8Fe0.1Co0.1VO4Composite oxides
In carrier, impregnate 2 hours, then 90 DEG C of water-bath fried drys, 120 DEG C are dried 8 hours, then roasted 5 hours under 350 DEG C of nitrogen atmospheres,
It is finally switched to 300 DEG C of air atmosphere to roast 4 hours, obtains the Pt-In-K/Ce of embodiment 30.8Fe0.1Co0.1VO4Catalyst.
(3) catalyst activity test condition is same as Example 1.The reactivity worth of catalyst is shown in Table 1.
Embodiment 4
(1)Ce0.8Fe0.1Co0.1VO4The preparation method of carrier is same as Example 1.
(2) according to Pt, In and K in Ce0.8Fe0.1Co0.1VO4Mass percentage in composite oxide carrier is respectively
2.0%, 0.05% and 0.10%.By the Pt (NO containing 2.0 grams of Pt3)2Solution, 0.17 gram of In (NO3)3·5H2O and 0.28 gram of lemon
Lemon acid potassium is diluted to 100ml with deionized water, is completely dissolved.Then 100g Ce is added0.8Fe0.1Co0.1VO4Composite oxides carry
It in body, impregnates 2 hours, then 90 DEG C of water-bath fried drys, 120 DEG C are dried 8 hours, roast 5 hours under last 350 DEG C of nitrogen atmospheres, so
After be switched to 300 DEG C of air atmosphere roast 4 hours, obtain the Pt-In-K/Ce of embodiment 40.8Fe0.1Co0.1VO4Catalyst.
(3) catalyst activity test condition is same as Example 1.The reactivity worth of catalyst is shown in Table 1.
Embodiment 5
(1)Ce0.8Fe0.1Co0.1VO4The preparation method of carrier is same as Example 1.
(2) according to Pt, In and K in Ce0.8Fe0.1Co0.1VO4Mass percentage in composite oxide carrier is respectively
2.0%, 0.10% and 0.05%.By the Pt (NO containing 2.0 grams of Pt3)2Solution, 0.34 gram of In (NO3)3·5H2O and 0.14 gram of lemon
Lemon acid potassium is diluted to 100ml with deionized water, is completely dissolved.It is then added to 100g Ce0.8Fe0.1Co0.1VO4Composite oxides
In carrier, impregnate 2 hours, then 90 DEG C of water-bath fried drys, 120 DEG C are dried 8 hours, then roasted 5 hours under 350 DEG C of nitrogen atmospheres,
It is finally switched to 300 DEG C of air atmosphere to roast 4 hours, obtains the Pt-In-K/Ce of embodiment 50.8Fe0.1Co0.1VO4Catalyst.
(3) catalyst activity test condition is same as Example 1.The reactivity worth of catalyst is shown in Table 1.
Embodiment 6
(1)Ce0.8Fe0.1Co0.1VO4The preparation method of carrier is same as Example 1.
(2) according to Pt, In and K in Ce0.8Fe0.1Co0.1VO4Mass percentage in composite oxide carrier is respectively
2.0%, 0.30% and 0.01%.By the Pt (NO containing 2.0 grams of Pt3)2Solution, 1.02 grams of In (NO3)3·5H2O and 0.028 gram
Potassium citrate is diluted to 100ml with deionized water, is completely dissolved.It is then added to 100g Ce0.8Fe0.1Co0.1VO4Combined oxidation
It in object carrier, impregnates 2 hours, then 90 DEG C of water-bath fried drys, 120 DEG C are dried 8 hours, and then roasting 5 is small under 350 DEG C of nitrogen atmospheres
When, it is finally switched to 300 DEG C of air atmosphere and roasts 4 hours, obtain the Pt-In-K/Ce of embodiment 60.8Fe0.1Co0.1VO4Catalysis
Agent.
(3) catalyst activity test condition is same as Example 1.The reactivity worth of catalyst is shown in Table 1.
Table 1: the activity that embodiment catalyst carbon monoxide and formaldehyde are eliminated
It can be seen that catalyst of the invention has preferable effect to carbon monoxide and formaldehyde catalytic removal under water vapour environment
Fruit, although the catalyst of embodiment 3 eliminates carbon monoxide and the effect of formaldehyde is best, precious metals pt comparision contents are high.?
In the embodiment that bullion content is 2%, the catalyst performance of embodiment 5 is best.Conversion in 1 hour and 10 hours is reacted in comparison
Rate, catalyst activity is obvious in addition to embodiment 1 declines, and other embodiments catalyst performance is more stable.
Claims (1)
1. it is a kind of under water vapour environment eliminate carbon monoxide and formaldehyde catalyst, it is characterised in that: the catalyst with
Ce0.8Fe0.1Co0.1VO4Composite oxides are carrier, Pt is that active component, In and K are co-catalyst composition;The matter of precious metals pt
Amount is Ce0.8Fe0.1Co0.1VO4The 1-3% of composite oxide carrier;The quality of co-catalyst In is Ce0.8Fe0.1Co0.1VO4It is compound
The 0.05-0.3% of oxide carrier;The quality of co-catalyst K is Ce0.8Fe0.1Co0.1VO4The 0.01- of composite oxide carrier
0.1%;The catalyst the preparation method comprises the following steps: using sol-gal process prepare Ce0.8Fe0.1Co0.1VO4Composite oxide carrier, so
Afterwards by Pt (NO3)2、In(NO3)3, potassium citrate mixed solution, with infusion process prepare Ce0.8Fe0.1Co0.1VO4Supporting Pt, In, K are urged
Agent,
Specifically comprise the following steps:
(1) by Ce (NO3)3·6H2O、Fe(NO3)3·9H2O、Co(NO3)3·6H2O、VOC2O4·5H2O and citric acid are according to rubbing
You are than being that 0.80:0.10:0.10:1.0:0.50 is dissolved in deionized water, in 90 DEG C of stirring in water bath to gel state after being completely dissolved,
Then 120 DEG C drying 8 hours finally roast 4 hours under 500 DEG C of air atmospheres, obtain Ce0.8Fe0.1Co0.1VO4Carrier;
(2) by Pt (NO3)2、In(NO3)3, potassium citrate mixed solution be added Ce0.8Fe0.1Co0.1VO4In carrier, impregnate 2 hours,
Then 90 DEG C of water-bath fried drys, 120 DEG C are dried 8 hours, are roasted 5 hours under last 350 DEG C of nitrogen atmospheres, are then switched to air atmosphere
300 DEG C roast 4 hours, obtain catalyst, and wherein the quality of precious metals pt is Ce0.8Fe0.1Co0.1VO4Composite oxide carrier
1-3%;The quality of co-catalyst In is Ce0.8Fe0.1Co0.1VO4The 0.05-0.3% of composite oxide carrier;Co-catalyst K's
Quality is Ce0.8Fe0.1Co0.1VO4The 0.01-0.1% of composite oxide carrier.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710006800.8A CN106807398B (en) | 2017-01-05 | 2017-01-05 | It is a kind of under water vapour environment eliminate carbon monoxide and the catalyst of formaldehyde and preparation method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710006800.8A CN106807398B (en) | 2017-01-05 | 2017-01-05 | It is a kind of under water vapour environment eliminate carbon monoxide and the catalyst of formaldehyde and preparation method thereof |
Publications (2)
Publication Number | Publication Date |
---|---|
CN106807398A CN106807398A (en) | 2017-06-09 |
CN106807398B true CN106807398B (en) | 2019-03-08 |
Family
ID=59110289
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710006800.8A Active CN106807398B (en) | 2017-01-05 | 2017-01-05 | It is a kind of under water vapour environment eliminate carbon monoxide and the catalyst of formaldehyde and preparation method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN106807398B (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109225239A (en) * | 2018-09-03 | 2019-01-18 | 金华职业技术学院 | CO oxidation catalyst and preparation method thereof under a kind of steam and carbon dioxide atmosphere |
CN110898834B (en) * | 2019-11-29 | 2022-08-12 | 金华铂锐催化科技有限公司 | Catalyst for eliminating volatile organic compounds and preparation method thereof |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101168126A (en) * | 2007-10-18 | 2008-04-30 | 清华大学 | Method for in-situ preparing three-effect catalyst by sol-gel method on honeycomb ceramic carrier |
CN101992101A (en) * | 2009-08-31 | 2011-03-30 | 中国石油化工股份有限公司上海石油化工研究院 | Precious metal catalyst |
EP2420316A1 (en) * | 2010-03-17 | 2012-02-22 | Samsung Electronics Co., Ltd. | Porous oxide catalyst and method of preparing the porous oxide catalyst |
CN103831111A (en) * | 2014-03-17 | 2014-06-04 | 上海应用技术学院 | Catalyst for low-temperature CO catalytic oxidation and preparation method of catalyst |
CN104226306A (en) * | 2014-10-14 | 2014-12-24 | 北京恒泰实达科技股份有限公司 | Catalyst for oxidizing and eliminating formaldehyde at room temperature and preparation method thereof |
CN105435814A (en) * | 2015-11-14 | 2016-03-30 | 无锡清杨机械制造有限公司 | Catalyzing composition for purifying air |
CN106000420A (en) * | 2016-06-03 | 2016-10-12 | 华烁科技股份有限公司 | Catalyst for integrated removal of N2O and NOx and preparation method thereof |
-
2017
- 2017-01-05 CN CN201710006800.8A patent/CN106807398B/en active Active
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101168126A (en) * | 2007-10-18 | 2008-04-30 | 清华大学 | Method for in-situ preparing three-effect catalyst by sol-gel method on honeycomb ceramic carrier |
CN101992101A (en) * | 2009-08-31 | 2011-03-30 | 中国石油化工股份有限公司上海石油化工研究院 | Precious metal catalyst |
EP2420316A1 (en) * | 2010-03-17 | 2012-02-22 | Samsung Electronics Co., Ltd. | Porous oxide catalyst and method of preparing the porous oxide catalyst |
CN103831111A (en) * | 2014-03-17 | 2014-06-04 | 上海应用技术学院 | Catalyst for low-temperature CO catalytic oxidation and preparation method of catalyst |
CN104226306A (en) * | 2014-10-14 | 2014-12-24 | 北京恒泰实达科技股份有限公司 | Catalyst for oxidizing and eliminating formaldehyde at room temperature and preparation method thereof |
CN105435814A (en) * | 2015-11-14 | 2016-03-30 | 无锡清杨机械制造有限公司 | Catalyzing composition for purifying air |
CN106000420A (en) * | 2016-06-03 | 2016-10-12 | 华烁科技股份有限公司 | Catalyst for integrated removal of N2O and NOx and preparation method thereof |
Non-Patent Citations (1)
Title |
---|
铂催化剂上HCHO、CO低温催化氧化研究;石艳芝;《中国优秀硕士学位论文全文数据库(工程科技Ⅰ辑)》;20120515(第 05 期);B027-225 |
Also Published As
Publication number | Publication date |
---|---|
CN106807398A (en) | 2017-06-09 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP6792055B2 (en) | Carbon composite material co-doped with transition metal and nitrogen used for formaldehyde purification and its preparation method | |
CN107398272B (en) | Composite carrier catalyst for room-temperature catalysis of formaldehyde and preparation method thereof | |
CN105363430B (en) | Titania oxide supported vanadic acid cerium zirconium denitrating catalyst, preparation method and application | |
CN100450610C (en) | Magnenese-cerium composite oxide supported catalyst for purifying formaldehyde in the indoor air | |
US9802180B2 (en) | Catalyst for synergistic control of oxynitride and mercury and method for preparing the same | |
CN106807398B (en) | It is a kind of under water vapour environment eliminate carbon monoxide and the catalyst of formaldehyde and preparation method thereof | |
CN101898137A (en) | Pd-Cu catalyst for CO low-temperature oxidation and preparation method thereof | |
CN110404526A (en) | Based on the derivative La of MOFs2O3The method that@C activates persulfate removal PPCPs and As (III) | |
CN103962174A (en) | AgCo bimetallic catalyst with adsorption-catalysis double functions for use in removal of formaldehyde and preparation method thereof | |
CN105944713B (en) | A kind of tungsten tin manganese-cerium composite oxide denitrating catalyst and its preparation and application | |
CN106423198B (en) | It is a kind of for eliminating the catalyst and preparation method thereof of carbon monoxide and formaldehyde | |
CN108187672A (en) | A kind of purifying formaldehyde material prepared based on ultrasonic atomization technique and preparation method | |
CN104907097A (en) | Room temperature efficient carbon monoxide removing catalysis material | |
EP0238700B1 (en) | Carbon monoxide oxidizing catalyst | |
CN101698149B (en) | Supported gold-PGM alloy catalyst with stable storage property and preparation method thereof | |
CN106040260A (en) | Catalyst for catalytic oxidation of carbonic oxide and preparation method of catalyst | |
CN102744063B (en) | Bio-reduction preparation method of palladium catalyst | |
CN104399499B (en) | For nonvalent mercury oxidation Cerium monophosphate is catalyst based, preparation method and application | |
JP6107487B2 (en) | N2O decomposition catalyst and N2O-containing gas decomposition method using the same | |
CN107252694B (en) | The catalyst and preparation method thereof of CO is aoxidized under a kind of steam and carbon dioxide atmosphere | |
TWI458549B (en) | Preparation of ceria-supported nano gold-silver catalysts and its application in carbon monoxide removal in air | |
CN104984757B (en) | A kind of preparation method of formaldehyde quick removal agent | |
CN105107501B (en) | Sulfur poisoning-resistant catalyst for handling vehicle exhaust and preparation method thereof | |
TWI484998B (en) | Catalyst for Decomposition of Volatile Organic Compounds and Their Preparation | |
CN104368339A (en) | Catalyst for concurrently and efficiently removing soot and NOx under oxygen-enriched, sulfur-containing and water-containing conditions, and preparation method thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |