CN101837295A - Load type ozone nanometer type reduction catalyst and manufacturing method thereof - Google Patents
Load type ozone nanometer type reduction catalyst and manufacturing method thereof Download PDFInfo
- Publication number
- CN101837295A CN101837295A CN200910300925A CN200910300925A CN101837295A CN 101837295 A CN101837295 A CN 101837295A CN 200910300925 A CN200910300925 A CN 200910300925A CN 200910300925 A CN200910300925 A CN 200910300925A CN 101837295 A CN101837295 A CN 101837295A
- Authority
- CN
- China
- Prior art keywords
- nitrate
- reduction catalyst
- catalyst
- load type
- deionized water
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Classifications
-
- 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
Abstract
The invention relates to a reduction catalyst technology, in particular to a load type ozone nanometer type reduction catalyst and a manufacturing method thereof. The invention is characterized in that each kilogram of superfine or nano activated carbon is added with 27g-725g of manganous nitrate, 73g-590g of copper nitrate, 0.019g-0.093g of palladium nitrate and 650g-850g of deionized water, and the mixture is dipped for 0.5 to 1 hour, dried in a constant temperature drying device, then roasted for certain time at set temperature and manufactured into the load type nano catalyst after being cooled.
Description
Technical field
The present invention relates to a kind of reducing catalyst technology, especially relate to a kind of load type ozone nanometer type reduction catalyst and manufacture method thereof.
Background technology
Ozone is widely used in fields such as sterilization, deodorizing, wastewater treatment, and just directly enter atmosphere has certain threat to health to the ozone that has not consumed under not processed situation.Also can produce ozone in the modern electrical equipment, also will directly influence surrounding air by the ozone that corona discharge and electrion produce, have a strong impact on our healthy such as cabin, duplicator, printing machine, facsimile machine, sterilizing machine etc.Reducing catalyst preparation method kind in the market is more, each have their own performance characteristics.
As the patent No. is a ZL01105215.5 support type ozone (O
3) reducing catalyst and manufacture method thereof, it is characterized in that every 1KG column-shaped active carbon, add 140G~180G ferric nitrate, 120G~180G nickel nitrate, 0.002G~0.020G silver nitrate, 0.00001G~0.00020G palladium nitrate, 700ML~780ML deionized water, use deionized water dipping, in stainless container while rotating the oven dry macerate, temperature is controlled at 100 ℃~140 ℃, then 360 ℃~380 ℃ roasting temperatures 2~4 hours, naturally after the cooling, with 12 eye mesh screens screenings, loaded catalyst.
And for example the patent No. is that ZL01138151.5 has invented a kind of catalyst and preparation technology thereof who eliminates ozone and nitrogen oxide, and manganese nitrate, copper nitrate, nickel nitrate and silver nitrate are made nitrate solution; Placing nitrate solution to soak the back catalyst carrier takes out oven dry, places nitrogen to heat; Again catalyst carrier is placed nitrogen, hydrogen mixed gas heating back cool to room temperature.
Also be the preparation method and the equipment of a ZL200710118756.6 load type metal nanocatalyst just like the patent No., be under supersonic induced condition, with measuring pump with metal salt solution by the micropore on the hollow ceramic membrane tube wall be diffused into by reducing agent and carrier material form mixture slurry solution in, make metal ion absorbing and reducing on the catalyst carrier surface, centrifugation then, the precipitate with deionized water washing forms the load type metal nanocatalyst after oven dry and the calcination.
Summary of the invention
The objective of the invention is in order to solve the existing anti-steam poor-performing of reducing catalyst, the problem that service life is long, provide a kind of cost suitably, stable performance, durability be strong, can remove the Catalysts and its preparation method of ozone fast.
Above-mentioned technical problem of the present invention is mainly solved by following technical proposals: this load type ozone nanometer type reduction catalyst and manufacture method thereof, it is characterized in that every kilogram of ultra-fine or nano active carbon, add 27g~725g manganese nitrate, 73g~590g copper nitrate, 0.019g~0.093g palladium nitrate, 650g~850g deionized water, flooded 0.5~1 hour, in freeze-day with constant temperature equipment, dry, then at the roasting temperature regular hour of setting, the loaded nano level catalyst of making after the cooling.
As preferably, described is carrier with ultra-fine or nano active carbon, is that the major catalyst palladium nitrate is secondary catalyst with manganese nitrate, copper nitrate, uses deionized water dipping, and each part is by certain proportioning.
As preferably, described in freeze-day with constant temperature equipment temperature be controlled at 100 ℃~120 ℃.
As preferably, described nitrate with manganese nitrate or copper or palladium is dissolved in the deionized water, immerse behind the activated carbon in freeze-day with constant temperature equipment 100 ℃~120 ℃ dry down, then 350 ℃~450 ℃ roasting temperatures of setting 2~4 hours.
Implementation result of the present invention is: anti-steam performance is good, reaches 1500-2500 hour service life, can reach ozone fully and send out exhaust emissions index 50ppb.
Therefore, the present invention be a kind of cost suitably, stable performance, durability be strong, can remove the Catalysts and its preparation method of ozone fast.
The specific embodiment
Below by embodiment, technical scheme of the present invention is described in further detail.
In the present embodiment, the carrier of catalyst adopts ultra-fine or nano level active carbon, and active component is a major catalyst by 2~20% manganese dioxide and 2~15% cupric oxide, and 0.01~0.02% palladium oxide is that secondary catalyst is formed.
The preparation method adopts dipping~roasting method preparation, the nitrate that is about to manganese nitrate and copper or palladium is dissolved in deionized water, immerse behind ultra-fine or the nano active carbon in 100 ℃~120 ℃ dry down, again 350 ℃~450 ℃ roasting temperatures 2~4 hours, the cooling back loaded nano level catalyst.
As get the 188g manganese nitrate, the 293g copper nitrate, 0.04g palladium nitrate, the 700ml deionized water, these several nitrate are dissolved in the deionized water, got in the deionized water that 1kg superfine active carbon dust is impregnated into mixed nitrate 1.5 hours, dry down in 100 ℃~120 ℃, 350 ℃~450 ℃ roasting temperatures 2.5 hours, promptly get Nano type load ozone reduction catalyst after the cooling again.
The characteristics of this catalyst are that anti-steam performance is good, long service life 1500-2500 hour, can reach ozone fully and send out exhaust emissions index 50ppb.
The foregoing description is to explanation of the present invention, is not limitation of the invention, any structure after the simple transformation of the present invention is all belonged to protection scope of the present invention.
Claims (4)
1. load type ozone nanometer type reduction catalyst and manufacture method thereof, it is characterized in that every kilogram of ultra-fine or nano active carbon, add 27g~725g manganese nitrate, 73g~590g copper nitrate, 0.019g~0.093g palladium nitrate, 650g~850g deionized water, flooded 0.5~1 hour, in freeze-day with constant temperature equipment, dry, under the temperature of setting, carry out roasting, the loaded nano level catalyst of making after the cooling then.
2. a kind of load type ozone nanometer type reduction catalyst according to claim 1 and manufacture method thereof, it is characterized in that with ultra-fine or nano active carbon be carrier, with manganese nitrate, copper nitrate is that the major catalyst palladium nitrate is secondary catalyst, use deionized water dipping, each part is by certain proportioning.
3. a kind of load type ozone nanometer type reduction catalyst according to claim 1 and manufacture method thereof is characterized in that temperature is controlled at 100 ℃~120 ℃ in freeze-day with constant temperature equipment.
4. a kind of load type ozone nanometer type reduction catalyst according to claim 1 and manufacture method thereof, it is characterized in that the nitrate of manganese nitrate or copper or palladium is dissolved in the deionized water, immerse behind the activated carbon in freeze-day with constant temperature equipment 100 ℃~120 ℃ dry down, then 350 ℃~450 ℃ roasting temperatures of setting 2~4 hours.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2009103009257A CN101837295B (en) | 2009-03-18 | 2009-03-18 | Load type ozone nanometer type reduction catalyst and manufacturing method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2009103009257A CN101837295B (en) | 2009-03-18 | 2009-03-18 | Load type ozone nanometer type reduction catalyst and manufacturing method thereof |
Publications (2)
Publication Number | Publication Date |
---|---|
CN101837295A true CN101837295A (en) | 2010-09-22 |
CN101837295B CN101837295B (en) | 2013-01-09 |
Family
ID=42741109
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN2009103009257A Active CN101837295B (en) | 2009-03-18 | 2009-03-18 | Load type ozone nanometer type reduction catalyst and manufacturing method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN101837295B (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102126781A (en) * | 2011-04-20 | 2011-07-20 | 中国石油天然气集团公司 | Method for treating reverse osmosis concentrates of petrochemical wastewater |
CN107876044A (en) * | 2017-10-26 | 2018-04-06 | 上海交通大学 | Nano composite material catalyst and its production and use |
-
2009
- 2009-03-18 CN CN2009103009257A patent/CN101837295B/en active Active
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102126781A (en) * | 2011-04-20 | 2011-07-20 | 中国石油天然气集团公司 | Method for treating reverse osmosis concentrates of petrochemical wastewater |
CN102126781B (en) * | 2011-04-20 | 2013-09-11 | 中国石油天然气集团公司 | Method for treating reverse osmosis concentrates of petrochemical wastewater |
CN107876044A (en) * | 2017-10-26 | 2018-04-06 | 上海交通大学 | Nano composite material catalyst and its production and use |
Also Published As
Publication number | Publication date |
---|---|
CN101837295B (en) | 2013-01-09 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN111054178B (en) | Formaldehyde removal purification material and preparation method and application thereof | |
CN105478136B (en) | A kind of catalyst of cooperating with low-temperature plasma-catalytic degraded industrial organic exhaust gas and preparation method and application | |
CN103381363B (en) | Catalysts and its preparation method, the purposes of deozonize and harmful organic substance simultaneously | |
CN108554402B (en) | Application of manganese dioxide/carbon cloth composite material and air purification device | |
CN104646020A (en) | Ozone catalyst and preparation method | |
CN103084184A (en) | Manganese-iron composite oxide supported catalyst for removing ozone in indoor air | |
CN102513123B (en) | Rare-earth perovskite type catalyst for treating industrial waste gas as well as preparation method and application thereof | |
CN103586026A (en) | Carbon supported catalyst for ozone oxidation, and preparation method and use thereof | |
CN109012740A (en) | Molecular sieve catalyst, preparation method and application for microwave catalysis oxidation processing organic wastewater | |
CN108816244B (en) | Nano carbon-based composite material for catalytic oxidation degradation of formaldehyde and preparation method and application thereof | |
CN109382107A (en) | Ozone oxidation catalyst and preparation method thereof based on absorbent charcoal carrier | |
CN107213907B (en) | Preparation method of foam nickel-based in-situ mesoporous catalytic oxidation catalyst | |
CN104998542A (en) | Electric heating device with catalytic coating and preparation method and application thereof | |
CN103706359B (en) | A kind of Low-temperature catalyst eliminating halides and preparation method | |
CN102489305A (en) | Transition metal composite oxide catalyst for catalytic decomposition of N2O and method for preparing catalyst | |
CN102962064A (en) | Gamma-form alumina loaded metallic oxide catalyst as well as preparation method and application thereof | |
CN103816865B (en) | A kind of organic exhaust gas adsorption scavenging agent and its preparation method | |
CN105327699A (en) | Air cleaning material | |
CN109289917A (en) | Alkali modification removes the preparation method of formaldehyde composite catalyst | |
CN101837295B (en) | Load type ozone nanometer type reduction catalyst and manufacturing method thereof | |
CN102188977A (en) | Method for preparing high-efficiency ammonia decomposition catalyst | |
CN109304184A (en) | A kind of activated carbon loaded iron-manganese-copper denitrating catalyst and its preparation method and application | |
CN109796014A (en) | It is a kind of using ferric nitrate as the preparation method of the mesoporous activated carbon of activator | |
JPWO2016167172A1 (en) | Deodorizing filter | |
CN106311222A (en) | Double-transition metal-based silkworm excrement porous carbon catalyst and preparation method thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
TR01 | Transfer of patent right |
Effective date of registration: 20210406 Address after: 315000 no.933, lingxu 2nd Road, Binhai Economic Development Zone, Cixi City, Ningbo City, Zhejiang Province Patentee after: NINGBO YOUMING ELECTRICAL APPLIANCE Co.,Ltd. Address before: 315200 No. 47 Renmin Road, Zhenhai District, Zhejiang, Ningbo, China Patentee before: Ningbo Zhenhai Yuanda Electromechanical Manufacturing Co.,Ltd. |
|
TR01 | Transfer of patent right |