CN103691423A - Preparation method for high-activity cellular nitrogen oxide removal catalyst - Google Patents
Preparation method for high-activity cellular nitrogen oxide removal catalyst Download PDFInfo
- Publication number
- CN103691423A CN103691423A CN201310620683.6A CN201310620683A CN103691423A CN 103691423 A CN103691423 A CN 103691423A CN 201310620683 A CN201310620683 A CN 201310620683A CN 103691423 A CN103691423 A CN 103691423A
- Authority
- CN
- China
- Prior art keywords
- percent
- preparation
- content
- nitrogen oxide
- catalyst
- 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.)
- Pending
Links
Landscapes
- Catalysts (AREA)
Abstract
The invention relates to the field of catalysts, and discloses a preparation method for a high-activity cellular nitrogen oxide removal catalyst. The preparation method is characterized by comprising the following steps: putting weighed TiO2 powder, SiO2, WO3 and V2O5 into a material mixing machine and stirring; adding a small amount of ammonia water and water in the process of stirring to adjust the PH value of the materials to be greater than 7; adding glass fiber and a trace amount of carboxymethyl cellulose, polyoxyethylene and sesbania powder, mixing by using a mixing machine to finally obtain a material which is suitable for extrusion molding, wherein the material mainly comprises the components of 68 to 92.8 percent of TiO2, 3 to 10 percent of SiO2, 2 to 10 percent of glass fiber, 2 to 10 percent of WO3, and 0.2 to 2 percent of V2O5. Due to the adoption of the technical scheme, the catalyst has the advantages of high mechanical strength, high wear-resistant strength, high temperature resistance, high activity and the like, can function under specific flue gas conditions, and can be widely applied to denitration devices such as low and high-dust thermal power plants.
Description
Technical field
The present invention relates to catalyst field, is the preparation method that a kind of high activity honeycomb fashion removes nitrogen oxide catalyst.
Background technology
Power plants nitrogen oxide generation accounts for 50% of national total release, and nitrogen oxide is the main reason that forms acid rain and photochemical fog in atmosphere, serious harm natural environment and human health.In September, 2011,21 Chinese Ministry of Environmental Protection issued < < fossil-fuel power plant atmospheric pollutant emission standard > >, and the concentration of emission limit value unification of domestic nitrogen oxide is defined as 100mg/m
3, the new-built unit time of implementation, the old unit time of implementation, this concentration of emission limit value required for national all regions from July, 2014 from 2012.Current, the mainstream technology of denitrating flue gas is SCR SCR technology in the world, and its core is SCR catalyst.
As far back as the seventies in last century, developed country just starts, according to situations such as national emission level, coal characteristics, boiler types, to have developed a series of SCR catalyst as Japan, Germany, the U.S. etc.At present, the experience of the many R&D institutions of China or individual foreign, complicated for Coal Combustion in China ature of coal, (for example flue-gas temperature is interval 360 ℃ ~ 450 ℃, and domestic coal-fired dustiness is up to 50-60g/Nm for the non-constant of boiler smoke condition after burning
3deng, flue gas NOx is up to 750mg) etc. situation, carry out the research of catalyst, and developed a series of denitrating catalysts.
Currently take the compositions such as TiO2 as main, V2O5 is denitrating catalyst active component.Simultaneously V2O5 is also the active component of SO2 oxidation side reaction, so the content of V2O5 is subject to the restriction of SO2 oxygenation efficiency, is not therefore increasing on the basis of V2O5 content, and adjusting formula, to improve catalyst activity will be the important breakthrough that catalyst is made.
Summary of the invention
The object of this invention is to provide and do not increasing on the basis of V2O5 content, adjust the preparation method that honeycomb fashion that formula improves catalyst activity removes nitrogen oxide catalyst, this catalyst is mainly with nano-TiO
2for main component, add certain auxiliary agent and pore former and active component, thereby make this catalyst there is bimodal pore distribution structure.
Technical scheme of the present invention is: a kind of high activity honeycomb fashion removes the preparation method of nitrogen oxide catalyst, it is characterized in that making step is:
A by take TiO
2powder, SiO
2, WO
3and V
2o
5put into batch mixer, stir; In whipping process, add a small amount of ammoniacal liquor and water, make the pH value of its material be greater than 7;
B adds carboxymethyl cellulose, polyethylene glycol oxide, the sesbania powder of glass fibre and trace, with batch mixer, mixes, and finally blends the material that is applicable to extrusion molding;
It is 150mm * 150mm that c extrudes sectional area with vacuum-extruder by above-mentioned material, and hole count is 18 * 18, the honeycomb fashion idiosome that length is 1000mm;
D is dried 7 ~ 15 days by idiosome under the condition of 30 ~ 70 ℃ of temperature, humidity 20 ~ 100%;
E calcines dried idiosome 8 ~ 15 hours under 250 ~ 300 ℃ of conditions, then under 380 ~ 420 ℃ of conditions, calcine 5 ~ 10 hours, finally under 580 ~ 620 ℃ of conditions, calcine 8 ~ 12 hours, thereby obtain a kind of highly active honeycomb fashion NO_x removal catalyst agent product.
Its main component TiO
2content is 68 ~ 92.8%, SiO
2content is 3%-10%, and content of glass fiber is 2%-10%, WO
3content is 2% ~ 10%, V
2o
5content is 0.2% ~ 2%.
Owing to having adopted technique scheme, this catalyst mechanical strength is high, wear strength is strong, high temperature resistant, active advantages of higher.Can under specific flue gas condition, move, can extensively apply in the denitrification apparatus such as low, high dust thermal power plant.
The specific embodiment
Below in conjunction with embodiment, the present invention is further illustrated.
Embodiment 1
By the TiO of the 10Kg taking
2the SiO of powder, 500g
2, 0.4Kg WO
3and the V of 70g
2o
5, put into batch mixer, stir; In whipping process, add a small amount of ammoniacal liquor and water, make the pH value of its material be greater than 7;
Add 0.5Kg glass fibre, 20g carboxymethyl cellulose, 30g polyethylene glycol oxide, 20g sesbania powder, with batch mixer, mix 2 ~ 4h, finally blend the material that is applicable to extrusion molding;
With vacuum-extruder, above-mentioned material being extruded to sectional area is 150mm * 150mm, and hole count is 20 * 20, the honeycomb fashion idiosome that length is 1000mm;
Idiosome is dried to 7 ~ 15 days under the condition of 30 ~ 70 ℃ of temperature, humidity 20 ~ 100%;
Dried idiosome is calcined 8 ~ 15 hours under 250 ~ 300 ℃ of conditions, then under 380 ~ 420 ℃ of conditions, calcined 5 ~ 10 hours, finally under 580 ~ 620 ℃ of conditions, calcine 8 ~ 12 hours, thereby obtain suitable catalyst.
Claims (2)
1. high activity honeycomb fashion removes a preparation method for nitrogen oxide catalyst, it is characterized in that making step is:
A by take TiO
2powder, SiO
2, WO
3and V
2o
5put into batch mixer, stir; In whipping process, add a small amount of ammoniacal liquor and water, make the pH value of its material be greater than 7;
B adds carboxymethyl cellulose, polyethylene glycol oxide, the sesbania powder of glass fibre and trace, with batch mixer, mixes, and finally blends the material that is applicable to extrusion molding;
It is 150mm * 150mm that c extrudes sectional area with vacuum-extruder by above-mentioned material, and hole count is 18 * 18, the honeycomb fashion idiosome that length is 1000mm;
D is dried 7 ~ 15 days by idiosome under the condition of 30 ~ 70 ℃ of temperature, humidity 20 ~ 100%;
E calcines dried idiosome 8 ~ 15 hours under 250 ~ 300 ℃ of conditions, then under 380 ~ 420 ℃ of conditions, calcine 5 ~ 10 hours, finally under 580 ~ 620 ℃ of conditions, calcine 8 ~ 12 hours, thereby obtain a kind of highly active honeycomb fashion NO_x removal catalyst agent product.
2. a kind of high activity honeycomb fashion according to claim 1 removes the preparation method of nitrogen oxide catalyst, it is characterized in that its main component TiO
2content is 68 ~ 92.8%, SiO
2content is 3%-10%, and content of glass fiber is 2%-10%, WO
3content is 2% ~ 10%, V
2o
5content is 0.2% ~ 2%.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310620683.6A CN103691423A (en) | 2013-11-29 | 2013-11-29 | Preparation method for high-activity cellular nitrogen oxide removal catalyst |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310620683.6A CN103691423A (en) | 2013-11-29 | 2013-11-29 | Preparation method for high-activity cellular nitrogen oxide removal catalyst |
Publications (1)
Publication Number | Publication Date |
---|---|
CN103691423A true CN103691423A (en) | 2014-04-02 |
Family
ID=50353182
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201310620683.6A Pending CN103691423A (en) | 2013-11-29 | 2013-11-29 | Preparation method for high-activity cellular nitrogen oxide removal catalyst |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN103691423A (en) |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103962126A (en) * | 2014-05-25 | 2014-08-06 | 华东理工大学 | Catalyst for selectively catalyzing and reducing nitrogen oxides and preparation method thereof |
CN104549311A (en) * | 2014-12-30 | 2015-04-29 | 安徽省元琛环保科技有限公司 | Special non-toxic denitration catalyst for coal-fired power plant and preparation method of special non-toxic denitration catalyst |
CN104971715A (en) * | 2015-06-30 | 2015-10-14 | 郑州康宁特环保装备科技有限公司 | Preparation method for cellular thin-walled denitration catalyst |
CN105289580A (en) * | 2015-10-12 | 2016-02-03 | 安徽迪诺环保新材料科技有限公司 | Soaking type low-temperature honeycomb flue gas catalyst and preparation method thereof |
CN106311301A (en) * | 2016-08-19 | 2017-01-11 | 安徽元琛环保科技股份有限公司 | Super-wear-resistant cellular denitration catalyst and preparation method thereof |
CN114713292A (en) * | 2022-05-05 | 2022-07-08 | 安徽工程大学 | End face treating agent, preparation method and application thereof, and end face treatment method after catalyst regeneration |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101502796A (en) * | 2009-03-20 | 2009-08-12 | 无锡市宜刚耐火材料有限公司 | Integral honeycomb selective catalytic reduction catalyst for flue gas denitration and method for preparing the same |
CN101676024A (en) * | 2008-09-17 | 2010-03-24 | 晶锐瓷业(北京)有限公司 | Faviform ammonia-method selective-catalytic-reduction denitrified catalyst and preparation method thereof |
CN103143396A (en) * | 2013-03-04 | 2013-06-12 | 郑州康宁特环保工程技术有限公司 | Honeycomb flue gas denitrification catalyst and preparation method thereof |
-
2013
- 2013-11-29 CN CN201310620683.6A patent/CN103691423A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101676024A (en) * | 2008-09-17 | 2010-03-24 | 晶锐瓷业(北京)有限公司 | Faviform ammonia-method selective-catalytic-reduction denitrified catalyst and preparation method thereof |
CN101502796A (en) * | 2009-03-20 | 2009-08-12 | 无锡市宜刚耐火材料有限公司 | Integral honeycomb selective catalytic reduction catalyst for flue gas denitration and method for preparing the same |
CN103143396A (en) * | 2013-03-04 | 2013-06-12 | 郑州康宁特环保工程技术有限公司 | Honeycomb flue gas denitrification catalyst and preparation method thereof |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103962126A (en) * | 2014-05-25 | 2014-08-06 | 华东理工大学 | Catalyst for selectively catalyzing and reducing nitrogen oxides and preparation method thereof |
CN104549311A (en) * | 2014-12-30 | 2015-04-29 | 安徽省元琛环保科技有限公司 | Special non-toxic denitration catalyst for coal-fired power plant and preparation method of special non-toxic denitration catalyst |
CN104971715A (en) * | 2015-06-30 | 2015-10-14 | 郑州康宁特环保装备科技有限公司 | Preparation method for cellular thin-walled denitration catalyst |
CN105289580A (en) * | 2015-10-12 | 2016-02-03 | 安徽迪诺环保新材料科技有限公司 | Soaking type low-temperature honeycomb flue gas catalyst and preparation method thereof |
CN106311301A (en) * | 2016-08-19 | 2017-01-11 | 安徽元琛环保科技股份有限公司 | Super-wear-resistant cellular denitration catalyst and preparation method thereof |
CN114713292A (en) * | 2022-05-05 | 2022-07-08 | 安徽工程大学 | End face treating agent, preparation method and application thereof, and end face treatment method after catalyst regeneration |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN103691423A (en) | Preparation method for high-activity cellular nitrogen oxide removal catalyst | |
CN102350340B (en) | Composite smoke denitration catalyst capable of oxidizing zero-valence mercury | |
CN103143396B (en) | Honeycomb flue gas denitrification catalyst and preparation method thereof | |
CN104162349B (en) | A kind of low-temperature denitration catalyst SO that suppresses2Poisoning method | |
CN101474581B (en) | Catalyst module edge hardening liquid with activity | |
CN105013474B (en) | The preparation method of metal oxide denitrating catalyst with orderly hierarchical porous structure | |
CN103691422A (en) | Preparation method of low-sulfur-dioxide honeycomb-type catalyst for removing nitrogen oxides | |
CN104437540A (en) | Phosphorus-resistant low-temperature SCR denitration catalyst and preparation method thereof | |
CN102366722A (en) | Denitrition catalyst with mercury removal effect and its preparation method | |
CN103433033A (en) | Low-temperature denitration catalyst MnOx-CeO2-TiO2-Al2O3, and preparation method and application thereof | |
CN107174934A (en) | A kind of new dry process rotary kiln liquid nano catalytic desulfurizing agent and preparation method thereof | |
CN102773090A (en) | Integral honeycomb denitration catalyst for novel WO3 addition technology and preparation method of catalyst | |
CN105363434A (en) | Manganese based SCR catalyst for low temperature denitration and preparation method thereof | |
CN103143345A (en) | Composite catalyst for catalytically oxidizing nitrogen oxide and preparation method of composite catalyst | |
CN103816799A (en) | Denitration agent capable of improving SNCR (Selective Non Catalytic Reduction) denitration efficiency and preparation method of denitration agent | |
CN103816909A (en) | Low-temperature denitrification catalyst and preparation method thereof | |
CN104001497B (en) | A kind of wide temperature window denitrating catalyst and its preparation method and application | |
CN103706390A (en) | Titanium-base carrier load vanadium phosphorus oxide catalyst for catalyzing oxidation of NO and preparation method of catalyst | |
CN108236960A (en) | A kind of TiO2-SO42-High resistant to sulfur ceria-based denitration catalyst of load and preparation method thereof | |
CN104128188A (en) | Denitration catalyst used in waste incineration power plant and preparation method thereof | |
CN103920503B (en) | A kind of modification regeneration SCR denitration and preparation method thereof | |
CN102188889A (en) | Device and method for combined removal of sulphur dioxide (SO2), nitrogen oxide (NOX) and mercury from fume | |
CN202410497U (en) | Flue gas denitration device of cement kiln | |
CN103537273B (en) | Denitrating catalyst of a kind of collaborative demercuration and preparation method thereof | |
CN104148095A (en) | Denitration and demercuration 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 | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20140402 |
|
WD01 | Invention patent application deemed withdrawn after publication |