CN106944130A - A kind of SCR AOC combination catalysts of purification of diesel tail gas and preparation method thereof - Google Patents

A kind of SCR AOC combination catalysts of purification of diesel tail gas and preparation method thereof Download PDF

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Publication number
CN106944130A
CN106944130A CN201710136961.9A CN201710136961A CN106944130A CN 106944130 A CN106944130 A CN 106944130A CN 201710136961 A CN201710136961 A CN 201710136961A CN 106944130 A CN106944130 A CN 106944130A
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aoc
scr
molecular sieve
purification
tail gas
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王秀庭
孙亮
季燕军
张�杰
王刚
岳军
贾莉伟
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Wuxi Weifu Environmental Protection Catalyst Co Ltd
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Wuxi Weifu Environmental Protection Catalyst 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
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/82Phosphates
    • B01J29/84Aluminophosphates containing other elements, e.g. metals, boron
    • B01J29/85Silicoaluminophosphates [SAPO compounds]
    • 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
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9404Removing only nitrogen compounds
    • B01D53/9409Nitrogen oxides
    • B01D53/9413Processes characterised by a specific catalyst
    • B01D53/9418Processes characterised by a specific catalyst for removing nitrogen oxides by selective catalytic reduction [SCR] using a reducing agent in a lean exhaust gas
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/80Mixtures of different zeolites
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2229/00Aspects of molecular sieve catalysts not covered by B01J29/00
    • B01J2229/10After treatment, characterised by the effect to be obtained
    • B01J2229/18After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself
    • B01J2229/186After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself not in framework positions
    • 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
    • Y02TCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
    • Y02T10/00Road transport of goods or passengers
    • Y02T10/10Internal combustion engine [ICE] based vehicles
    • Y02T10/12Improving ICE efficiencies

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Combustion & Propulsion (AREA)
  • Crystallography & Structural Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Exhaust Gas After Treatment (AREA)
  • Catalysts (AREA)

Abstract

The present invention relates to SCR AOC combination catalysts of a kind of purification of diesel tail gas and preparation method thereof, belong to catalyst preparation technical field.Including carrier, coating on AOC priming coats and SCR is coated with the carrier;The coated weight of the AOC priming coats is 50 150g/L, and the AOC priming coats include platinum-group noble metals, refractory oxide and the first molecular sieve;Wherein the coated weight of platinum-group noble metals is 0.01 1g/L, and the refractory oxide is 60% the 99% of AOC priming coat quality, and first molecular sieve is 1% the 40% of AOC priming coat quality;The coated weight of coating is 100 300g/L on the SCR, and the upper coatings of the SCR include the second molecular sieve of cupric, and wherein the mass fraction of copper is 0.1% 8%.Preparation method of the present invention is simple, and step is easily operated, and AOC priming coats and coating on the SCR that can be used in nitrous oxides selectivity catalysis reduction for ammoxidation function are respectively coated in catalyst carrier, and the using effect of catalyst is good.

Description

A kind of SCR-AOC combination catalysts of purification of diesel tail gas and preparation method thereof
Technical field
The present invention relates to a kind of SCR-AOC combination catalysts of purification of diesel tail gas and preparation method thereof, belong to catalysis Agent preparing technical field.
Background technology
Contain nitrogen oxides in the pollutant of diesel engine emissions(NOx), particulate matter(PM)And it is imperfect combustion Carbon monoxide(CO)And hydro carbons(HC).NOx mainly includes nitric oxide(NO)And nitrogen dioxide(NO2).It is well known that NOxIt is shape A series of one of compound into photochemical fog and acid rain, so as to trigger health and environmental problem.Accordingly, it would be desirable to by NOxAlso Originally it was N2And other poisonous and harmful substances are not generated, could eliminate NOx in motor-vehicle tail-gas to the unfavorable of the mankind and environment Influence.
SCR technology(SCR)It is that reducing agent is used under excess oxygen(Such as H2、HC、NH3/ urea)Will NOx selective reductions are N2And H2O, is the one preferred technique of NOx catalytic eliminatings in exhaust gas from diesel vehicle.NH3- SCR reactivities compared with Height, and its active window is also of a relatively high.At present, NH3- SCR technology has been successfully applied in diesel car tail gas refining, and It disclosure satisfy that the motor-vehicle tail-gas NO of Europe VIxDischarge standard.NOxWith NH3The key reaction occurred in SCR catalyst is:
4NH3 + 4NO + O2 → 4N2 + 6H2O
2NH3 + NO + NO2 → 2N2 + 3H2O
4NH3 + 3NO2 → 3.5N2 + 6H2O
4NH3 + 3O2 → 2N2 + 6H2O
In order to obtain the conversion rate of NOx of maximum, it is necessary to add the NH higher than stoichiometry into atmosphere3, but unreacted ammonia Gas can cause secondary pollution, and this phenomenon is commonly referred to as " NH_3 leakage ".In addition, ammonia(Particularly its aqueous solution)With corrosion Property, ammoniacal liquor can generate caustic mixture in gas extraction system condensed downstream, damage gas extraction system.Therefore, preferably in NH3Pass through row Eliminated before tracheae, in order to by excessive NH3It is converted into N2, the purpose for reducing NH_3 leakage is reached, many business gas extraction system exist SCR catalyst downstream is mounted with ammoxidation catalyst(AMOx), also referred to as NH_3 leakage catalyst(AOC).
Therefore, NOx can be eliminated by SCR by researching and developing a kind of catalyst article, while by excessive NH3Selective oxidation is N2, selective ammonia oxidation catalyst need there is sufficiently high NH in wider temperature range3Conversion ratio, and produce at least Nitrogen oxides is the research emphasis of this area.
The content of the invention
The invention aims to solve the above problems, there is provided a kind of SCR-AOC of purification of diesel tail gas combinations Catalyst and preparation method thereof, the catalyst prepared can eliminate the NOx in diesel engine vent gas and reduce the escaping of ammonia.
The present invention is adopted the following technical scheme that:A kind of SCR-AOC combination catalysts of purification of diesel tail gas, including carry Coating on AOC priming coats and SCR is coated with body, the carrier;
The coated weight of the AOC priming coats be 50-150g/L, the AOC priming coats include platinum-group noble metals, refractory oxide and First molecular sieve;Wherein the coated weight of platinum-group noble metals is 0.01-1g/L, and the refractory oxide is AOC priming coat quality 60%-99%, first molecular sieve is the 1%-40% of AOC priming coat quality;
The coated weight of coating is that coating includes the second molecular sieve of cupric on 100-300g/L, the SCR on the SCR, wherein The mass fraction of copper is 0.1%-8%.
The platinum-group noble metals are noble metal platinum and/or palladium, and the mass ratio of platinum palladium is 1:0-1.
The carrier is cordierite honeycomb ceramic or iron-chromium-aluminum metal honeycomb, the hole density of the carrier for 100-600 mesh/ Square inch.
The refractory oxide is aluminum oxide, magnesia, silica, titanium dioxide, cupric oxide, zirconium oxide, titanium dioxide One or more of mixtures in cerium.
First molecular sieve of stating is Y type molecular sieve, ZSM-5 molecular sieve, beta-molecular sieve, SAPO-34 molecular sieves or SSZ-13 One kind in molecular sieve.
Second molecular sieve is Cu/SAPO-34 molecular sieves or Cu/SSZ-13 molecular sieves.
The preparation method of the SCR-AOC combination catalysts of described purification of diesel tail gas, comprises the following steps:
(1)The preparation of AOC priming coat slurries:Refractory oxide and the first molecular sieve are added in deionized water, fire resisting oxidation The mass ratio of the gross mass and deionized water of thing and molecular sieve is 1-2:3, stir, form slurries;It is milled to granularity D90 At 5-15 μm, slurries are made;
Noble metal mass fraction is added in slurries for 10%-20% noble metal nitrate solution, wherein the nitric acid of noble metal Salting liquid is 1 with grind slurries quality ratio:10-1000, and stir, form AOC priming coat slurries;Then AOC priming coats are starched Liquid is coated on carrier according to 50-150 g solidfied materials/L coated weight;
(2)The drying roasting of AOC priming coats:By step(1)Gained is coated with the carrier of AOC priming coats and done at 100-150 DEG C It is dry 6-10 hours, it is calcined 1-3 hours at 500-600 DEG C, is cooled to room temperature stand-by;
(3)The preparation of the upper coating slurries of SCR:Second molecular sieve is added in deionized water, the matter of molecular sieve and deionized water Amount is than being 1:1-3, stirs to form slurries;Granularity D90 is milled at 5-15 μm, coating slurry on SCR is made;
(4)The drying roasting of the upper coatings of SCR:By step(3)Prepare coating slurry on gained SCR solid for 100-300g by coated weight Compound/L, which is coated to, to be loaded with the carrier of AOC priming coats, is dried 6-10 hours at 100-150 DEG C, at 500-600 DEG C Roasting 1-3 hours, that is, obtain the SCR-AOC combination catalysts of purification diesel engine tail gas.
The Cu/SAPO-34 molecular sieves or Cu/SSZ-13 molecular sieves prepared according to patent CN103818927A
The preparation method of the SCR-AOC combination catalysts of purification of diesel tail gas, comprises the following steps:
(1)The preparation of AOC priming coat slurries:Refractory oxide and molecular sieve are added in deionized water, refractory oxide and The gross mass of molecular sieve and the mass ratio of deionized water are 1:3-2:3, stir, form slurries;Granularity D90 is milled to exist 5-15 μm, coating slurry is made;
(2)Precious metal solution is added in coating slurry and stirred, AOC priming coat slurries is formed, AOC priming coats is starched Liquid is quantitatively coated on carrier;
(3)The drying roasting of AOC priming coats:It is coated with the carrier of AOC priming coats to dry 8 hours at 120 DEG C, at 550 DEG C Roasting 2 hours, is cooled to room temperature stand-by;
(4)The preparation of the upper coating slurries of SCR:Cu/SAPO-34 molecular sieves or Cu/SSZ-13 molecular sieves are added to deionized water In, the mass ratio of molecular sieve and deionized water is 1:3-1:1, stir to form slurries;Granularity D90 is milled in 5-15 μ M, is made coating slurry on SCR;
(5)The drying roasting of the upper coatings of SCR:Coating slurry on SCR is coated to by coated weight for 100-300g/L and has been loaded with On the carrier of AOC priming coats, dried 8 hours at 120 DEG C, be calcined 2 hours at 550 DEG C, that is, obtain purification diesel engine tail gas SCR-AOC combination catalysts.
Beneficial effects of the present invention:Preparation method of the present invention is simple, and step is easily operated, is respectively coated in catalyst carrier There are the AOC priming coats and coating, catalyst on the SCR that can be used in nitrous oxides selectivity catalysis reduction for ammoxidation function Using effect it is good.
Brief description of the drawings
Fig. 1 is the embodiment of the present invention 1 and 2 in NH3NH under oxidation reaction condition3Conversion ratio.
Fig. 2 is the embodiment of the present invention 1 and 2 in NH3N under oxidation reaction condition2Selectivity.
Embodiment
Below in conjunction with specific embodiment, the present invention is further illustrated.
Embodiment 1
A kind of SCR-AOC combination catalysts of purification of diesel tail gas, catalyst carrier is carrier cordierite ceramic, and volume is 1.236L, hole density is 400 mesh/square inch;Coating is included in coating on AOC priming coats and SCR, AOC priming coats on carrier Containing cerium-zirconium-aluminium composite oxide, beta-molecular sieve and precious metals pt, the coated weight of AOC priming coats is 100g/L, precious metals pt Load capacity is 0.15g/L.The upper coating compositions of SCR are Cu/SAPO-34 molecular sieves, and Cu mass fractions are 3.0%, Cu/SAPO-34 points Son sieve is made according to patent CN103818927A, and the coated weight of the upper coatings of SCR is 120g/L.
Preparation method comprises the following steps:
(1)The preparation of AOC catalyst floors:98.7g ceriums-zirconium-aluminium composite oxide, 24.7g beta-molecular sieves are added to In 197.5g deionized waters, stir, form slurries makes granularity D90 be 10 μm through ball milling;
The preparation method of cerium-zirconium-aluminium composite oxide:It is 1 first by the mass ratio of cerium oxide and aluminum oxide:9 prepare cerium- In aluminium composite oxide, then cerium-zirconium-aluminum composite oxide is prepared by the method for incipient impregnation by by cerium-aluminium composite oxide Thing;Zirconyl nitrate solution, dipping, at then standing 12 hours, 120 DEG C are configured by the saturated extent of adsorption of cerium-aluminium composite oxide Drying is calcined 2 hours for 8 hours, 550 DEG C.The matter of zirconium oxide and cerium-aluminium composite oxide wherein in cerium-zirconium-aluminium composite oxide Amount is than being 1:7;
1.26g platinum nitrate solutions are added in above-mentioned slurries(14.71 wt% Pt), slurries are all coated to after stirring On carrier, obtain being coated with the carrier of AOC priming coats;
(2)The drying roasting of AOC priming coats:By step(1)It is small that gained is coated with the drying 8 at 120 DEG C of the carrier of AOC priming coats When, 550 DEG C are calcined 2 hours;
(3)The preparation of the upper coating slurries of SCR:148.3g Cu/SAPO-34 molecular sieves are added in 296.6g deionized waters, stirred Mix uniform, form slurries;Make the granularity D90 of slurries be 10 μm through ball milling, coating slurry on SCR is made;
(4)The drying roasting of the upper coatings of SCR:Coating slurry is all coated on obtained AOC priming coats, done at 120 DEG C Dry 8 hours, it is calcined 2 hours at 550 DEG C, that is, obtains the SCR-AOC combination catalysts of purification diesel engine tail gas.
Embodiment 2
Specific preparation method and active testing and example 1 are essentially identical, and difference is the Cu/SSZ-13 with copper content 3.0% Molecular sieve replaces Cu/SAPO-34 molecular sieves.
The innovative point of the present invention is being applied in combination for SCR catalyst and AOC catalyst, here primarily to being presented two Plant main flow NH3- SCR catalyst(Cu/SAPO-34 and Cu/SSZ-13)With the effect after AOC catalyst combination uses.
NH3 oxidation activities are evaluated
The NH3 oxidation activities of catalyst in embodiment are evaluated in 150-500 DEG C of Temperature Programmed Processes, evaluates and is included in atmosphere 300 ppm NH3、10% O2、5% H2O、5% CO2, use N2It is used as Balance Air.Volume space velocity is 100000h-1.Use Fourier Leaf transformation infrared spectrum(FTIR)Analyzer detection outlet production concentration, thus calculates conversion ratio and the product selection of reactant Property.
Fig. 1 describes the embodiment of the present invention 1 and 2 in NH3NH under oxidation reaction condition3Conversion ratio.In 200-230 DEG C of temperature In the range of degree, the NH of 2 embodiments3Conversion ratio is almost identical;In 260-500 DEG C of temperature range, the NH of 2 embodiments3Conversion Rate is both greater than 90%.
Fig. 2 describes the embodiment of the present invention 1 and 2 in NH3N under oxidation reaction condition2Selectivity.In 200-255 DEG C of temperature In the range of, the N of 2 embodiments2Select similar temperament;In 255-500 DEG C of temperature range, Cu/SSZ-13 embodiment 2 is used N2Selectivity is higher than the embodiment 1 using Cu/SAPO-34, in addition, the N in 310-490 DEG C of temperature range of embodiment 22Selectivity More than 80%.

Claims (7)

1. a kind of SCR-AOC combination catalysts of purification of diesel tail gas, it is characterised in that:Including carrier, applied on the carrier It is covered with coating on AOC priming coats and SCR;
The coated weight of the AOC priming coats be 50-150g/L, the AOC priming coats include platinum-group noble metals, refractory oxide and First molecular sieve;Wherein the coated weight of platinum-group noble metals is 0.01-1g/L, and the refractory oxide is AOC priming coat quality 60%-99%, first molecular sieve is the 1%-40% of AOC priming coat quality;
The coated weight of coating is that coating includes the second molecular sieve of cupric on 100-300g/L, the SCR on the SCR, wherein The mass fraction of copper is 0.1%-8%.
2. the SCR-AOC combination catalysts of purification of diesel tail gas as claimed in claim 1, it is characterised in that:The platinum family Noble metal is noble metal platinum and/or palladium, and the mass ratio of platinum palladium is 1:0-1.
3. the SCR-AOC combination catalysts of purification of diesel tail gas as claimed in claim 1, it is characterised in that:The carrier For cordierite honeycomb ceramic or iron-chromium-aluminum metal honeycomb, the hole density of the carrier is 100-600 mesh/square inch.
4. the SCR-AOC combination catalysts of purification of diesel tail gas as claimed in claim 1, it is characterised in that:The fire resisting Oxide is the one or more in aluminum oxide, magnesia, silica, titanium dioxide, cupric oxide, zirconium oxide, ceria Mixture.
5. the SCR-AOC combination catalysts of purification of diesel tail gas as claimed in claim 1, it is characterised in that:It is described to state One molecular sieve is one kind in Y type molecular sieve, ZSM-5 molecular sieve, beta-molecular sieve, SAPO-34 molecular sieves or SSZ-13 molecular sieves.
6. the SCR-AOC combination catalysts of purification of diesel tail gas as claimed in claim 1, it is characterised in that:Described second Molecular sieve is Cu/SAPO-34 molecular sieves or Cu/SSZ-13 molecular sieves.
7. the preparation method of the SCR-AOC combination catalysts of the purification of diesel tail gas described in claim 1, it is characterised in that: Comprise the following steps:
(1)The preparation of AOC priming coat slurries:Refractory oxide and the first molecular sieve are added in deionized water, fire resisting oxidation The mass ratio of the gross mass and deionized water of thing and molecular sieve is 1-2:3, stir, form slurries;It is milled to granularity D90 At 5-15 μm, slurries are made;
Noble metal mass fraction is added in slurries for 10%-20% noble metal nitrate solution, wherein the nitric acid of noble metal Salting liquid is 1 with grind slurries quality ratio:10-1000, and stir, form AOC priming coat slurries;Then AOC priming coats are starched Liquid is coated on carrier according to 50-150 g solidfied materials/L coated weight;
(2)The drying roasting of AOC priming coats:By step(1)Gained is coated with the carrier of AOC priming coats and done at 100-150 DEG C It is dry 6-10 hours, it is calcined 1-3 hours at 500-600 DEG C, is cooled to room temperature stand-by;
(3)The preparation of the upper coating slurries of SCR:Second molecular sieve is added in deionized water, the matter of molecular sieve and deionized water Amount is than being 1:1-3, stirs to form slurries;Granularity D90 is milled at 5-15 μm, coating slurry on SCR is made;
(4)The drying roasting of the upper coatings of SCR:By step(3)Prepare coating slurry on gained SCR solid for 100-300g by coated weight Compound/L, which is coated to, to be loaded with the carrier of AOC priming coats, is dried 6-10 hours at 100-150 DEG C, at 500-600 DEG C Roasting 1-3 hours, that is, obtain the SCR-AOC combination catalysts of purification diesel engine tail gas.
CN201710136961.9A 2017-03-09 2017-03-09 A kind of SCR AOC combination catalysts of purification of diesel tail gas and preparation method thereof Pending CN106944130A (en)

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CN108355707A (en) * 2018-02-05 2018-08-03 无锡威孚环保催化剂有限公司 A kind of preparation method of CuSAPO-34 molecular sieves series catalysts
CN109261200A (en) * 2018-09-30 2019-01-25 无锡威孚环保催化剂有限公司 NH_3 leakage catalyst and preparation method thereof for equivalent burn natural gas engines
JP2019035340A (en) * 2017-08-10 2019-03-07 いすゞ自動車株式会社 Exhaust emission control system
CN110075907A (en) * 2019-05-08 2019-08-02 中自环保科技股份有限公司 A kind of ammoxidation catalyst and preparation method thereof for diesel car tail gas refining
CN111939988A (en) * 2020-08-25 2020-11-17 湖南省吉安特技术有限公司 Method for improving catalytic performance of nano diesel engine tail gas in SCR temperature zone
CN112536061A (en) * 2019-09-23 2021-03-23 中国石油化工股份有限公司 Exhaust gas treatment catalyst and preparation method thereof
CN112536031A (en) * 2019-09-23 2021-03-23 中国石油化工股份有限公司 Catalyst for treating industrial waste gas and preparation method thereof
CN112675901A (en) * 2020-12-29 2021-04-20 惠州市瑞合环保科技有限公司 SCR catalyst for diesel engine tail gas treatment and preparation method and application thereof
CN113751082A (en) * 2021-09-27 2021-12-07 苏州松之源环保科技有限公司 Coating method of non-noble metal SDPF double-coating catalyst
CN114425416A (en) * 2020-10-10 2022-05-03 中国石油化工股份有限公司 Ammonia conversion catalyst and preparation method and application thereof
CN114904570A (en) * 2022-01-20 2022-08-16 安徽艾可蓝环保股份有限公司 High-nitrogen selective ammonia oxidation catalyst applied to diesel engine and preparation method thereof
WO2023028928A1 (en) * 2021-09-01 2023-03-09 宁波吉利罗佑发动机零部件有限公司 Ammonia adsorption catalyst, and preparation method therefor and use thereof

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CN103442805A (en) * 2011-03-31 2013-12-11 恩亿凯嘉股份有限公司 Ammonia oxidation catalyst, exhaust gas purification device using same, and exhaust gas purification method
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Cited By (17)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2019035340A (en) * 2017-08-10 2019-03-07 いすゞ自動車株式会社 Exhaust emission control system
CN108355707A (en) * 2018-02-05 2018-08-03 无锡威孚环保催化剂有限公司 A kind of preparation method of CuSAPO-34 molecular sieves series catalysts
CN109261200A (en) * 2018-09-30 2019-01-25 无锡威孚环保催化剂有限公司 NH_3 leakage catalyst and preparation method thereof for equivalent burn natural gas engines
CN110075907A (en) * 2019-05-08 2019-08-02 中自环保科技股份有限公司 A kind of ammoxidation catalyst and preparation method thereof for diesel car tail gas refining
CN112536061A (en) * 2019-09-23 2021-03-23 中国石油化工股份有限公司 Exhaust gas treatment catalyst and preparation method thereof
CN112536031A (en) * 2019-09-23 2021-03-23 中国石油化工股份有限公司 Catalyst for treating industrial waste gas and preparation method thereof
CN112536061B (en) * 2019-09-23 2023-05-02 中国石油化工股份有限公司 Exhaust gas treatment catalyst and preparation method thereof
CN112536031B (en) * 2019-09-23 2022-10-11 中国石油化工股份有限公司 Catalyst for treating industrial waste gas and preparation method thereof
CN111939988A (en) * 2020-08-25 2020-11-17 湖南省吉安特技术有限公司 Method for improving catalytic performance of nano diesel engine tail gas in SCR temperature zone
CN114425416B (en) * 2020-10-10 2023-11-03 中国石油化工股份有限公司 Ammonia conversion catalyst and preparation method and application thereof
CN114425416A (en) * 2020-10-10 2022-05-03 中国石油化工股份有限公司 Ammonia conversion catalyst and preparation method and application thereof
CN112675901A (en) * 2020-12-29 2021-04-20 惠州市瑞合环保科技有限公司 SCR catalyst for diesel engine tail gas treatment and preparation method and application thereof
WO2023028928A1 (en) * 2021-09-01 2023-03-09 宁波吉利罗佑发动机零部件有限公司 Ammonia adsorption catalyst, and preparation method therefor and use thereof
CN115843275A (en) * 2021-09-01 2023-03-24 宁波吉利罗佑发动机零部件有限公司 Ammonia adsorption catalyst and preparation method and application thereof
CN115843275B (en) * 2021-09-01 2024-02-06 宁波吉利罗佑发动机零部件有限公司 Ammonia adsorption catalyst, preparation method and application thereof
CN113751082A (en) * 2021-09-27 2021-12-07 苏州松之源环保科技有限公司 Coating method of non-noble metal SDPF double-coating catalyst
CN114904570A (en) * 2022-01-20 2022-08-16 安徽艾可蓝环保股份有限公司 High-nitrogen selective ammonia oxidation catalyst applied to diesel engine and preparation method thereof

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