CN107126973A - A kind of in-situ synthetic method of catalyst of CuFe SAPO 34 and its application - Google Patents

A kind of in-situ synthetic method of catalyst of CuFe SAPO 34 and its application Download PDF

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CN107126973A
CN107126973A CN201710398412.9A CN201710398412A CN107126973A CN 107126973 A CN107126973 A CN 107126973A CN 201710398412 A CN201710398412 A CN 201710398412A CN 107126973 A CN107126973 A CN 107126973A
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catalyst
sapo
source
cufe
crystallization
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谢利娟
阮文权
邓芸
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Jiangnan University
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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
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B37/00Compounds having molecular sieve properties but not having base-exchange properties
    • C01B37/06Aluminophosphates containing other elements, e.g. metals, boron
    • C01B37/08Silicoaluminophosphates [SAPO compounds], e.g. CoSAPO
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B39/00Compounds having molecular sieve and base-exchange properties, e.g. crystalline zeolites; Their preparation; After-treatment, e.g. ion-exchange or dealumination
    • C01B39/54Phosphates, e.g. APO or SAPO compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/20Reductants
    • B01D2251/206Ammonium compounds
    • B01D2251/2062Ammonia
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/01Engine exhaust gases
    • B01D2258/012Diesel engines and lean burn gasoline engines

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Abstract

The invention discloses a kind of in-situ synthetic method of catalyst of CuFe SAPO 34 and its application, belong to catalysis technical field.The inventive method comprises the following steps:Boehmite is added in deionized water and is stirred dissolving, orthophosphoric acid and fumed silica is then added, mantoquita and TEPA are added after mixing, Fe salt and n-propylamine are added after being sufficiently stirred for;It will stir after the completion of complete gel is fitted into crystallization in hydrothermal reaction kettle, crystallization and be cooled to room temperature, solid crystallized product will be separated with mother liquor, it is washed with deionized to neutrality, dry, be then calcined in atmosphere, obtain the small pore molecular sieve catalysts of CuFe SAPO 34.The present invention prepares the catalyst of CuFe SAPO 34 using one-step synthesis, by preferred Fe load capacity, significantly improves the catalytic performance and low temperature water repelling property of the catalyst of Cu SAPO 34.

Description

A kind of in-situ synthetic method of CuFe-SAPO-34 catalyst and its application
Technical field
The present invention relates to a kind of in-situ synthetic method of CuFe-SAPO-34 catalyst and its application, belong to catalysis technique neck Domain.
Background technology
NOxThe atmosphere polluting problems such as haze, acid rain, photochemical fog can be caused, be atmosphere pollution important at present, It is the key object of the current China's prevention and control of air pollution of China.The combustion of fossil fuel that people's industrial production and life activity are brought It is nitrogen oxides (NOx) main source.In artificial source NOxIn discharge, using coal-fired plant flue gas as the stationary source of representative and diesel oil Tail gas is the NO of the moving source of representativexOccupy about 60% discharge share.With the raising of national Abgasgesetz standard, move Dynamic source NOxThe processing method that emission compliance need to be combined using internal purification technology and post-processing technology.Wherein post-processing approach Improvement is the major way for the standard that reply is improved constantly.SCR technology (Selective in post processing Catalytic Reduction, SCR) there are removal efficiency height, low cost and other advantages, obtain more concern.SCR technology is just Refer under conditions of catalyst is present, NH is sprayed into flue gas3, urea or other reducing agents, make its optionally with NOxInstead N should be generated2, without with O2Generation non-selective oxidation, so as to reach reduction NOxReduction temperature, raising NOxThe mesh of purification efficiency 's.The core of SCR technology is the outstanding catalyst of catalytic performance.
At present V is still in the catalyst of China's wide popularization and application2O5-WO3(MoO3)/TiO2.The catalyst is extensive Applied to stationary source coal-fired flue gas denitration, and it is also introduced into exhaust gas from diesel vehicle control field.But the catalyst system use Still there are many problems in diesel car tail gas refining.For qualified discharge, in moving source exhaust treatment system, SCR processing systems are past It is combined toward needs with particulate matter trap (DPF).It is thus desirable to which SCR catalyst can bear the high temperature brought during dpf regeneration (being higher than 700 DEG C) and the environment of high humility, i.e. catalyst needs to have excellent hydrothermal stability.But V2O5-WO3(MoO3)/ TiO2Volatilization and the carrier TiO of vanadium can occur more than 600 DEG C for catalyst2Phase transformation, so the catalyst be not suitable for temperature compared with High motor-driven vehicle gas disposal, it is impossible to meet tomorrow requirement.The bio-toxicity of other vanadium also limit its use.Other researchs More ripe is the different degrees of presence temperature of catalyst series such as Cu bases or Fe bases prepared by carrier with ZSM-5, beta and Y etc. Spend action pane narrow, the problems such as poor and anti-HC poisoning capabilities of hydrothermal stability are poor.Therefore, the NH of environment-friendly high-efficiency is developed3- SCR is urged Agent is very urgent.
Small pore molecular sieve catalyst is current NH3The study hotspot in-SCR fields, wherein the Cu-SAPO- with CHA structure 34 catalyst are the representatives of such molecular sieve catalyst, and such catalyst is provided simultaneously with high activity, high N2It is selective and excellent Hydrothermal stability.But such catalyst is more sensitive to the environment of cold aqueous, and sulfur poisoning resistance is poor, to practical application It is unfavorable.So, further improve the catalyst and be very important.
Cu and Fe are loaded on SAPO-34 carriers with liquid-phase ion exchange by 2012100717231 patent disclosure Preparing compound small pore molecular sieve catalyst is used for NOx catalytic purifications.But this method complex steps, it is necessary to repeatedly load, and gold Belong to load capacity to be difficult to control.The low temperature water repelling property and sulfur poisoning resistance of gained catalyst are also without relevant report.
The content of the invention
In order to solve the above problems, an object of the present invention is that provide one kind prepares CuFe- by in-situ synthesis The preparation method of SAPO-34 catalyst, catalyst is made by hydrothermal synthesis method, is small pore molecular sieve class catalyst.The present invention Method it is simple to operation, gained catalyst has excellent NH3- SCR catalytic performances, can be used for moving source NH3- SCR denitration Process.In addition, the catalyst of the selective catalyst reduction of nitrogen oxides prepared, operation temperature window is wide, with excellent N2Generation selectivity and hydrothermal stability, are highly suitable for the purification of nitrogen oxides in exhaust gas from diesel vehicle.
The in-situ synthesis method for preparing CuFe-SAPO-34 catalyst of the present invention, be by silicon source, water, phosphorus source, silicon source, Cu sources, TEPA, and source of iron are mixed evenly, and then add template, continue to stir;Complete gel dress will be stirred Enter crystallization in hydrothermal reaction kettle, crystallization is cooled down after terminating;Solid crystallized product is separated with mother liquor, washs, dry, roast Burn, that is, obtain CuFe-SAPO-34 small pore molecular sieve catalysts.
In one embodiment, source of aluminium can be boehmite AlOOH, alundum (Al2O3), sodium metaaluminate etc..
In one embodiment, phosphorus source is phosphoric acid.
In one embodiment, the silicon source is silica, Ludox etc..
In one embodiment, the Cu sources are Cu salt.
In one embodiment, the Cu salt is copper sulphate, copper nitrate, copper acetate, copper chloride, copper carbonate, cupric oxide Any one in or two or more combinations.
In one embodiment, the source of iron is molysite.
In one embodiment, the molysite is ferric nitrate, iron chloride, ferrous sulfate, ferric sulfate, frerrous chloride, lemon Any one in lemon acid iron etc. or two or more combinations.
In one embodiment, the template is n-propylamine (C3H9N), diethylamine, triethylamine, tetraethylamine hydroxide Any one in or two or more combinations.
In one embodiment, methods described, specifically includes following steps:
(1) boehmite is added in deionized water and stirred;
(2) phosphoric acid is added, is stirred;
(3) fumed silica is added to be stirred;
(4) after above-mentioned medicine is well mixed, Cu salt and TEPA are added;
(5) after being sufficiently mixed, molysite and n-propylamine are added, continues to stir.
(6) complete gel will be stirred and is fitted into crystallization in hydrothermal reaction kettle, crystallization is cooled to room temperature after terminating.Will be solid Body crystallized product is separated with mother liquor, is washed with deionized to neutrality, is dried, is then calcined, that is, obtains in air atmosphere CuFe-SAPO-34 small pore molecular sieve catalysts.
In one embodiment, methods described control silicon source, phosphorus source, silicon source, water, Cu sources, TEPA, source of iron, The mol ratio of template is (0.75-1.25):(0.75-1.25):(0.4-0.7):(70-80):(0.01-3.5):(0.01- 3.5):(0.001-0.1):(0.01-3.5).
In one embodiment, methods described control silicon source, phosphorus source, silicon source, water, Cu sources, TEPA, source of iron, The mol ratio of template is 1:1:0.57:77.17:0.12:0.12:(0.019-0.076):3.38.
In one embodiment, source of aluminium, phosphorus source, silicon source, water, Cu sources, TEPA, source of iron, template point Wei not AlOOH, H3PO4、SiO2、H2O, Cu salt, TEPA, Fe salt and n-propylamine.
In one embodiment, AlOOH, H3PO4、SiO2、H2O, Cu salt, TEPA, Fe salt and n-propylamine rub You are than being 1:1:0.57:77.17:0.12:0.12:0.057:3.38.
In one embodiment, the temperature of crystallization be 150-200 DEG C, such as 150,155,160,165,170,175, 180th, 185,190,195 or 200 DEG C.
In one embodiment, the time of the crystallization be 24-72h, such as 30,35,40,45,50,55,60, 65、72h。
In one embodiment, the time of the crystallization is 72h.
In one embodiment, the washing is to be washed with water to neutrality.
In one embodiment, the temperature of the drying be 80-120 DEG C, such as 80 DEG C, 90 DEG C, 100 DEG C, 110 DEG C, 120 ℃。
In one embodiment, the temperature of the drying is 100 DEG C.
In one embodiment, the time of the drying is 3-16 hours, such as 3h, 5h, 6h, 8h, 10h, 12h, 16h.
In one embodiment, the time of the drying is 12h.
In one embodiment, the roasting is calcined in air atmosphere.
In one embodiment, the temperature of the roasting be 550-800 DEG C, such as 550 DEG C, 600 DEG C, 650 DEG C, 700 DEG C, 800℃。
In one embodiment, the temperature of the roasting is 600 DEG C.
In one embodiment, the time of the roasting is 3-10 hours, such as 3h, 5h, 6h, 8h, 10h.
In one embodiment, the time of the roasting is 6h.
In one embodiment, the heating rate of the roasting be 0.5-5 DEG C/min, for example, 0.5,1,1.5,2, 2.5、3、3.5、4、4.5、5℃/min。
In one embodiment, the roasting heating rate is 1 DEG C/min.
In one embodiment, methods described specifically includes following steps:Boehmite is added in deionized water It is stirred, then adds orthophosphoric acid and fumed silica, mantoquita and TEPA is added after mixing, is sufficiently stirred for Fe salt and n-propylamine are added afterwards;It will stir after the completion of complete gel is fitted into crystallization in hydrothermal reaction kettle, crystallization and be cooled to Room temperature, solid crystallized product is separated with mother liquor, is washed with deionized to neutrality, is dried, be then calcined, obtain in atmosphere CuFe-SAPO-34 small pore molecular sieve catalysts;Wherein control AlOOH, H3PO4、SiO2、H2O, Cu salt, TEPA, Fe salt Mol ratio with n-propylamine is 1:1:0.57:77.17:0.12:0.019-0.076:3.38.Using catalyst tool obtained by the program There is excellent catalytic activity, it has the conversion rate of NOx higher than 80% in 300-500 DEG C, and significantly improves Cu- SAPO-34 low temperature water repelling property.
Second object of the present invention is to provide the CuFe-SAPO-34 small pore molecular sieves prepared according to the method described above Catalyst.
Third object of the present invention is to provide the application of the CuFe-SAPO-34 small pore molecular sieve catalysts.
In one embodiment, the application is to be used for catalyst nox.
In one embodiment, the application is to be used for NH3- SCR reacts.
In one embodiment, the application is nitrogen oxides in catalysis reduction exhaust gas from diesel vehicle.
Beneficial effects of the present invention:
(1) this method prepares CuFe-SAPO-34 small pore molecular sieve catalysts using in-situ synthesis, and further passes through The input amount of Fe salt is controlled to control the load capacity of Fe salt, to obtain NH3Point of-SCR catalytic activity and water resistant excellent in stability Sub- sieve catalyst;The preparation method of the CuFe-SAPO-34 is one-step synthesis, compared to the ion exchange in solution used at present Method is more easy and effective, without multistep ion-exchange step, economizes on resources.
(2) this method prepares gained catalyst using the cooperative effect between Cu and Fe, opens up the temperature window of catalyst The raising of width, particularly high temperature section activity is more notable, is more applicable for diesel car tail gas refining.
(3) catalyst prepared by this method improves its low temperature water resistant ability.
(4) catalyst prepared by this method improves sulfur poisoning resistance.
(5) catalyst of the invention is prepared using nontoxic component, and health and ecological environment will not be caused harm;System Preparation Method is simple to operation.
Brief description of the drawings
CuFe-SAPO-34 and Cu-SAPO-34 catalyst activity and water resistant poisoning capability ratio that Fig. 1 is prepared for the present invention Compared with;
The change for the CuFe-SAPO-34 and Cu-SAPO-34 catalyst sulfur poisoning resistances that Fig. 2 is prepared for the present invention.
Specific embodiment
In the present invention, following method is taken in the evaluation of catalyst:
CuFe-SAPO-34 molecular sieve catalysts are taken, are placed on activity rating fixed bed reactors, simulated exhaust composition For 500ppm NH3, 500ppm NO, 5vol%O2, N2For Balance Air, total flow is 500mL/min, and reaction velocity is 400000h-1
Here is that the present invention is specifically described.
Embodiment 1
Using boehmite AlOOH as silicon source, silica (SiO2) it is silicon source, phosphoric acid (H3PO4) it is phosphorus source, Cu-TEPA For Cu sources, Fe (NO3)3·9H2O is source of iron, and each raw material is mixed, and then adds n-propylamine (C3H9N it is) template, is stirred overnight Until stirring;Solution is put into reactor again, reactor is put into crystallization 3d in 180 DEG C of baking oven;Question response kettle fills Divide after cooling, stirring, which is stood, simultaneously filters out suction filtration after impurity, and the baking oven 3h that the sample after filtering is put into 105 DEG C is baked to;Again The sample of drying is put into Muffle furnace, 600 DEG C of roasting 6h are risen to 1 DEG C/min programming rate, one-step synthesis legal system is obtained Standby CuFe-SAPO-34 catalyst.Wherein, AlOOH, H are controlled3PO4、SiO2、H2O, Cu salt, TEPA, Fe salt and just The mol ratio of propylamine is 1:1:0.57:77.17:0.12::0.12:0.057:3.38.
Control:Without Fe salt, according to above-mentioned preparation method, Cu-SAPO-34 catalyst can be made.
Before and after investigation addition Fe salt, the low temperature water resistant capacity variation of catalyst, by catalyst containing 10%H2O air In atmosphere, through 70 DEG C of aging 16h, the catalyst performance change before and after detection aging.Fig. 1 provides catalyst performance before and after the addition of Fe salt Can change
From figure 1 it appears that the temperature window of CuFe-SAPO-34 catalyst is wider, can be in the range of 250-550 DEG C 70% conversion rate of NOx is remained above, most highly active can reach 90.3%.And the temperature window for compareing Cu-SAPO-34 is narrower, It is only capable of being remained above 60% conversion rate of NOx in the range of 250-350 DEG C, most highly active can reach 78.6%.
In addition, CuFe-SAPO-34 is after 70 DEG C of aging 16h, catalyst can be still remained above in the range of 300-500 DEG C 50% conversion rate of NOx.And Cu-SAPO-34 is compareed after the processing of identical aging condition, kept only in the range of 300-450 DEG C Conversion rate of NOx more than 30%.
By data above, it is known that this method not only improves the activity of catalyst, its low temperature water repelling property is also significantly improved.
Fig. 2 provides the situation of the sulfur poisoning resistance of catalyst before and after Fe is added, it is known that the CuFe-SAPO- after sulfur poisoning 34 catalyst can still remain larger than 60% conversion ratio at 350-500 DEG C, and highest conversion rate of NOx is 81.5%.But Cu-SAPO- 34 catalyst only remain larger than 60% conversion ratio at 400-500 DEG C, and highest conversion rate of NOx is 62.9%.
Embodiment 2
The present embodiment has investigated the performance of the CuFe-SAPO-34 catalyst obtained under different Fe salt additions.
The preparation method of catalyst:Fe dosage is adjusted, AlOOH, H is controlled3PO4、SiO2、H2O, Cu salt, four ethene five The mol ratio of amine, Fe salt and n-propylamine is respectively A (1:1:0.57:77.17:0.12:0.12:0.0095:3.38)、B(1:1: 0.57:77.17:0.12:0.12:0.019:3.38)、C(1:1:0.57:77.17:0.12:0.12:0.029:3.38)、D(1: 1:0.57:77.17:0.12:0.12:0.043:3.38).Remaining is same as Example 1.
The CuFe-SAPO-34 catalyst prepared, catalytic performance at different temperatures is as shown in table 1.
The catalytic performance of the catalyst obtained under the difference Fe additions of table 1
Embodiment 3
The present embodiment has investigated the performance of the CuFe-SAPO-34 catalyst obtained under different crystallization temperatures.
Control AlOOH, H3PO4、SiO2、H2O, Cu salt, TEPA, the mol ratio of Fe salt and n-propylamine are 1:1: 0.57:77.17:0.12::0.12:0.057:3.38, crystallization temperature is respectively 150 DEG C, 200 DEG C, and remaining is same as Example 1. The performance of the CuFe-SAPO-34 catalyst prepared is as shown in table 2.
The catalytic performance of the catalyst obtained under the different crystallization temperatures of table 2
Although the present invention is disclosed as above with preferred embodiment, it is not limited to the present invention, any to be familiar with this skill The people of art, without departing from the spirit and scope of the present invention, can do various changes and modification, therefore the protection model of the present invention Enclose being defined of being defined by claims.

Claims (10)

1. a kind of method that in-situ synthesis prepares CuFe-SAPO-34 catalyst, it is characterised in that methods described be by silicon source, Phosphorus source, silicon source, water, Cu sources, TEPA, and source of iron are mixed evenly, and then add template, continue to stir;It will stir Mix complete gel and be fitted into crystallization in hydrothermal reaction kettle, crystallization is cooled down after terminating;Solid crystallized product is separated with mother liquor, Washing, dry, roasting, that is, obtain CuFe-SAPO-34 small pore molecular sieve catalysts.
2. according to the method described in claim 1, it is characterised in that methods described control silicon source, phosphorus source, silicon source, water, Cu sources, TEPA, source of iron, the mol ratio of template are (0.75-1.25):(0.75-1.25):(0.4-0.7):(70-80): (0.01-3.5):(0.01-3.5):(0.001-0.1):(0.01-3.5).
3. according to the method described in claim 1, it is characterised in that methods described control silicon source, phosphorus source, silicon source, water, Cu sources, TEPA, source of iron, the mol ratio of template are 1:1:0.57:77.17:0.12:0.12:(0.019-0.076):3.38.
4. according to the method described in claim 1, it is characterised in that source of aluminium is boehmite AlOOH, alundum (Al2O3) Or sodium metaaluminate.
5. according to the method described in claim 1, it is characterised in that the source of iron is molysite, such as ferric nitrate, iron chloride, sulphur Any one in sour ferrous iron, ferric sulfate, frerrous chloride, ironic citrate or two or more combinations.
6. according to the method described in claim 1, it is characterised in that the Cu sources are Cu salt, such as copper sulphate, copper nitrate, vinegar Any one in sour copper, copper chloride, copper carbonate, cupric oxide or two or more combinations.
7. according to the method described in claim 1, it is characterised in that the temperature of crystallization is 150-200 DEG C.
8. the CuFe-SAPO-34 catalyst prepared according to any methods described of claim 1~7.
9. the application of CuFe-SAPO-34 catalyst described in claim 8.
10. application according to claim 9, it is characterised in that for NH3- SCR reacts.
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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110182827A (en) * 2019-05-27 2019-08-30 天津大学 A kind of preparation method and applications of CuM/SAPO-34 and Fe/Beta coupled molecule sieve
CN110193378A (en) * 2019-05-27 2019-09-03 天津大学 A kind of preparation method and applications of CuM/SAPO-34 molecular sieve
CN110479358A (en) * 2019-07-24 2019-11-22 西安交通大学 A kind of Cu-SAPO-34 molecular sieve denitrating catalyst and preparation method thereof that dysprosium is modified
WO2020098103A1 (en) * 2018-11-14 2020-05-22 福州大学 Preparation method and application of mesoporous fecu-zsm-5 molecular sieve
CN111330437A (en) * 2020-03-01 2020-06-26 北京化工大学 Method and system for cooperatively purifying multiple pollutants in adipic acid production
CN111437878A (en) * 2020-01-21 2020-07-24 大连理工大学盘锦产业技术研究院 Cu-SAPO-34 molecular sieve, preparation method thereof and application thereof in selective catalytic reduction denitration
CN113617387A (en) * 2021-09-14 2021-11-09 江西省生态环境科学研究与规划院 Iron source SAPO-34 catalyst with low-temperature SCR activity and preparation method and application thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101797518A (en) * 2010-04-14 2010-08-11 太原理工大学 Method for preparing monolithic catalyst for purification of diesel exhaust
CN102614910A (en) * 2012-03-16 2012-08-01 北京工业大学 Ammonia-selective preparation method of SAPO-34 supported Cu-Fe catalyst for catalytically removing NOx
CN104209141A (en) * 2014-09-24 2014-12-17 中国科学院生态环境研究中心 Cu-SAPO-34 molecular sieve catalyst and preparation method and application thereof
CN104722331A (en) * 2014-12-13 2015-06-24 济南大学 Preparation method of Cu-SAPO-44 microporous molecular sieve and application thereof as NH3-SCR catalyst
CN105413736A (en) * 2015-11-06 2016-03-23 中国第一汽车股份有限公司 Molecular sieve catalyst with wide temperature window and preparation method of catalyst
CN105523566A (en) * 2015-12-13 2016-04-27 定州市荣鼎水环境生化技术有限公司 Zeolite molecular sieve for selective catalytic reduction of nitrogen oxide by using ammonia as reducing agent and preparation method and application thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101797518A (en) * 2010-04-14 2010-08-11 太原理工大学 Method for preparing monolithic catalyst for purification of diesel exhaust
CN102614910A (en) * 2012-03-16 2012-08-01 北京工业大学 Ammonia-selective preparation method of SAPO-34 supported Cu-Fe catalyst for catalytically removing NOx
CN104209141A (en) * 2014-09-24 2014-12-17 中国科学院生态环境研究中心 Cu-SAPO-34 molecular sieve catalyst and preparation method and application thereof
CN104722331A (en) * 2014-12-13 2015-06-24 济南大学 Preparation method of Cu-SAPO-44 microporous molecular sieve and application thereof as NH3-SCR catalyst
CN105413736A (en) * 2015-11-06 2016-03-23 中国第一汽车股份有限公司 Molecular sieve catalyst with wide temperature window and preparation method of catalyst
CN105523566A (en) * 2015-12-13 2016-04-27 定州市荣鼎水环境生化技术有限公司 Zeolite molecular sieve for selective catalytic reduction of nitrogen oxide by using ammonia as reducing agent and preparation method and application thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
LEIMA 等: "Characterization of commercial Cu-SSZ-13 and Cu-SAPO-34 catalysts with hydrothermal treatment for NH3-SCR of NOx in diesel exhaust", 《CHEMICAL ENGINEERING JOURNAL》 *
张冉冉等: "Cu 基分子筛 NH3-SCR脱硝催化剂的研究进展", 《现代化工》 *

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020098103A1 (en) * 2018-11-14 2020-05-22 福州大学 Preparation method and application of mesoporous fecu-zsm-5 molecular sieve
CN110182827A (en) * 2019-05-27 2019-08-30 天津大学 A kind of preparation method and applications of CuM/SAPO-34 and Fe/Beta coupled molecule sieve
CN110193378A (en) * 2019-05-27 2019-09-03 天津大学 A kind of preparation method and applications of CuM/SAPO-34 molecular sieve
CN110193378B (en) * 2019-05-27 2022-02-11 天津大学 Preparation method and application of CuM/SAPO-34 molecular sieve
CN110182827B (en) * 2019-05-27 2022-08-12 天津大学 Preparation method and application of CuM/SAPO-34 and Fe/Beta coupled molecular sieve
CN110479358A (en) * 2019-07-24 2019-11-22 西安交通大学 A kind of Cu-SAPO-34 molecular sieve denitrating catalyst and preparation method thereof that dysprosium is modified
CN111437878A (en) * 2020-01-21 2020-07-24 大连理工大学盘锦产业技术研究院 Cu-SAPO-34 molecular sieve, preparation method thereof and application thereof in selective catalytic reduction denitration
CN111330437A (en) * 2020-03-01 2020-06-26 北京化工大学 Method and system for cooperatively purifying multiple pollutants in adipic acid production
CN113617387A (en) * 2021-09-14 2021-11-09 江西省生态环境科学研究与规划院 Iron source SAPO-34 catalyst with low-temperature SCR activity and preparation method and application thereof
CN113617387B (en) * 2021-09-14 2022-05-20 江西省生态环境科学研究与规划院 Iron source SAPO-34 catalyst with low-temperature SCR activity and preparation method and application thereof

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Application publication date: 20170905