CN105772098B - Catalyst for removing NOx by ammonia selective catalytic reduction and preparation method thereof - Google Patents

Catalyst for removing NOx by ammonia selective catalytic reduction and preparation method thereof Download PDF

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Publication number
CN105772098B
CN105772098B CN201610292200.8A CN201610292200A CN105772098B CN 105772098 B CN105772098 B CN 105772098B CN 201610292200 A CN201610292200 A CN 201610292200A CN 105772098 B CN105772098 B CN 105772098B
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molecular sieve
catalyst
catalytic reduction
preparation
removing nox
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CN105772098A (en
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张保才
王新昕
张楚宁
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NINGBO HIGH-TECH ZONE YONGSHI TECHNOLOGY Co Ltd
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Ningbo Fukai Purifier 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
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/26Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
    • B01J31/28Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of the platinum group metals, iron group metals or copper
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/56Foraminous structures having flow-through passages or channels, e.g. grids or three-dimensional monoliths

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

The invention discloses a preparation method of a catalyst for removing NOx by ammonia selective catalytic reduction, which comprises the following steps: (1) cation exchanging the molecular sieve with a salt solution of one or more metal cations by an ion exchange process; (2) after cation exchange, washing the molecular sieve with deionized water, drying at 50-200 ℃, and calcining at 200-600 ℃, so that cations exchanged into the molecular sieve are stably combined; (3) dispersing the molecular sieve treated in the step (2) in water, and mixing with a certain proportion of hollow alumina pellet powder, wherein the mass ratio of the molecular sieve to the hollow alumina pellet powder is from 2:1 to 15: 1, adding a binder and a thickening agent after fully dispersing, and then coating the mixture on a cordierite honeycomb carrier to form a catalyst coating with the thickness of tens of microns on the walls of fine pore channels of the honeycomb carrier. The catalyst prepared by the method is loaded by a molecular sieve, and has high-temperature activity and hydrothermal stability.

Description

The catalyst and preparation method thereof of NOx is removed for ammine selectivity catalytic reduction
Technical field
The invention belongs to the technical fields of tail gas denitrating catalyst, and in particular, the present invention relates to one kind being used for ammine selective The molecular sieve carried catalyst and preparation method thereof of catalysis reduction removing NOx.
Background technology
In diesel car engine tail gas containing hydrocarbon (HC), carbon monoxide (CO), nitrogen oxides (NOx) and The pernicious gases such as grain object (PM), tail gas itself have certain temperature, after first passing around direct oxidation catalyst (DOC), carbon Hydrogen compound and carbon monoxide are oxidized to the innocuous gas such as carbon dioxide and water, and nitrogen oxides and particulate matter cannot be converted, It subsequently enters in denitrifying catalyst with selective catalytic reduction (SCR catalyst), sprays urea liquid between the two catalyst, Urea is broken down into ammonia and carbon dioxide, and wherein ammonia reacts under the action of SCR catalyst with nitrogen oxides, generates The innocuous gas such as nitrogen and water.SCR catalyst, DOC catalyst and urea injection system are emphasis in this process.
There are mainly two types of the existing catalyst for ammine selectivity catalytic reduction removing oxynitrides.
The first is vanadium titanium tungsten oxide catalyst, and using titanium oxide as carrier, barium oxide is main active component, tungsten oxygen Compound then mainly plays a part of to improve catalyst hydrothermal stability as auxiliary agent.But the shortcomings that this catalyst, which is barium oxide, to be had Prodigious toxicity, no matter in catalyst production process, or after installation catalyst, it is de- that powder occurs at work for catalyst It falls, can all be caused to environment in very big harm, such as dust sucking human body.
Second is copper, iron, ZSM5 molecular sieve catalysts, and wherein ZSM5 molecular sieves are carrier, and copper and iron are active component. The shortcomings that this catalyst is that catalyst operating temperature section is narrow, and hydrothermal stability is poor, in actual operation due to diesel oil The presence of water in motor exhaust, copper and iron are easy to be lost in molecular sieve pore passage, to which catalytic activity reduces quickly.
Therefore, it is necessary to prepare it is a kind of there is more high activity and hydrothermal stability, and can in broader temperature range and SCR catalyst with high NOx conversion efficiency under conditions of high-speed.
Invention content
Technical problem to be solved by the invention is to provide a kind of molecular sieves removing NOx for ammine selectivity catalytic reduction Catalyst of load and preparation method thereof.The catalyst that the method for the present invention is prepared is that molecular sieve is load, is had higher High temperature active and hydrothermal stability;And there is high NOx conversion efficiency under conditions of broader temperature range and high-speed.
Technical solution is used by the present invention solves above-mentioned technical problem:NOx is removed for ammine selectivity catalytic reduction Catalyst preparation method, in turn include the following steps:
(1) salting liquid of molecular sieve and one or more kinds of metal cations is made to carry out cationic friendship by ion-exchange It changes.
(2) after cation exchanges, the molecular sieve is washed with deionized, then dry at 50~200 DEG C, then 200~600 DEG C of temperature lower calcinations combine to make to exchange to the cationic stabilized in molecular sieve;
(3) the step (2), treated that molecular sieve disperses in water, remixes into a certain proportion of hollow alumina Bead powder, the mass ratio of the molecular sieve and the hollow alumina bead powder is from 2:1 to 15:1, add after fully dispersed Enter adhesive and thickener, be then applied on cordierite honeycomb carrier, thickness is formed in the tiny cell walls of honeycomb substrate Tens microns of catalyst coat.
In above-mentioned technical proposal, in preferred embodiment, molecular sieve of the present invention is used with existing for aluminosilicate form ZSM-35 molecular sieve, silica alumina ratio are more than 30.Also, the ZSM-35 molecular sieve can be obtained by commercially available means, example The ZSM-35 molecular sieve produced such as Shanghai Shen Tan environmental friendly materials Co., Ltd.
In above-mentioned technical proposal, exchanged by cation, by original cation in molecular sieve, be substituted for active metal from Son constitutes catalytic reaction activity position to which active metallic ion to be introduced into molecular sieve pore passage.
In above-mentioned technical proposal, temperature, swap time and friendship when can be exchanged by adjusting metal cation salting liquid Number etc. is changed to control the amount of metal cation exchange.The basic pore passage structure of molecular sieve is constant after ion exchange.Specifically, originally Invention swaps under (20~25 DEG C) preferably at room temperature.Specifically, the operating procedure of the ion exchange is:By molecular sieve It is distributed to formation molecular sieve slurry in the water of room temperature, meanwhile, in another reaction kettle, the cation exchanged will be needed at room temperature Salt dissolves, and is subsequently poured into molecular sieve slurry, is stirred continuously, 1.5~4 hours;This process is 1 to 3 times repeatable.
In the step (1), the metal cation is copper ion, iron ion, titanium ion, vanadium ion and rare earth metal sun It is one or more in ion;The salting liquid is chloride, acetate, nitrate, sulfate or other halide.
In the step (1), metal cation and the molecular sieve ratio of exchange are from 0.5% to 40%.
Further include following steps before the step (1):By molecular sieve precalcining.The precalcining refer to 120~ It is calcined 0.5~1 hour at a temperature of 150 DEG C.It is handled by precalcining, removes having for molecular sieve pore passage and the template on surface Machine object, is more advantageous to ion exchange in this way.
In the step (2), dry drying time is 2~5 hours at described 50~200 DEG C;Described 200~600 DEG C The calcination time of temperature lower calcination is 2~8 hours.
In the step (3) of above-mentioned technical proposal, described adhesive is boehmite, and the thickener is ethoxy Cellulose.
In the step (3) of above-mentioned technical proposal, the specific painting method of " being coated to cordierite honeycomb carrier " is:Very Empty cladding process, upper end feed, vacuum valve is opened in posterior end within several seconds, under being inhaled slurry by negative pressure.
In one embodiment, the molecular sieve is one or both of ZSM-35 molecular sieve and Titanium Sieve Molecular Sieve.
In another embodiment, the molecular sieve is ZSM-22 molecular sieves, Cu-ZSM-5 molecular sieves, Beta molecular sieves In any one.
In preferred technical solution, the mass ratio of the molecular sieve and the hollow alumina bead powder is 8:1 To 10:1.It is further preferred that the mass ratio of the molecular sieve and the hollow alumina bead powder is 8:1.
The molecular sieve is ZSM-22 molecular sieves compared with prior art, the present invention having the following advantages that:
(1) it by the present invention in that being catalyst main carriers with ZSM-35 molecular sieve, and adulterates with hollow alumina bead With improve its dynamics distribution, by ion-exchange by copper ion, iron ion, titanium ion, vanadium ion and rare earth metal sun from Son is supported in molecular sieve pore passage, so that the catalyst that the present invention is prepared has higher high temperature active and hydro-thermal steady It is qualitative.
(2) catalyst that the present invention is prepared can have height under conditions of broader temperature range and high-speed NOx conversion efficiency.
Specific implementation mode
In order to better understand the content of the present invention, it is described further with reference to specific embodiment.It should be understood that these Embodiment is only used for that the present invention is further described, rather than limits the scope of the invention.In addition, it should also be understood that, having read this After the invention content, person skilled in art makes some nonessential changes or adjustment to the present invention, still falls within this The protection domain of invention.
Embodiment 1
For ammine selectivity catalytic reduction remove NOx molecular sieve carried catalyst preparation method, include successively with Lower step:
1, precalcining:ZSM-35 molecular sieve is calcined 0.5 hour at a temperature of 120 DEG C.It is handled, is removed by precalcining The organic matter of template on molecular sieve pore passage and surface is more advantageous to subsequent ion exchange in this way.
2, ion exchange:ZSM-35 molecular sieve after precalcining is distributed to formation molecular sieve slurry in the water of room temperature;Together When, in another reaction kettle, at room temperature by chlorination copper dissolution, it is subsequently poured into molecular sieve slurry, is stirred continuously, stirring 3 A hour.Wherein, the weight ratio of copper ion and ZSM-35 molecular sieve is 1%.
3, the molecular sieve after cation exchanges is washed with deionized, then 3 hours dry at 50 DEG C, then 500 DEG C of temperature lower calcinations 3 hours combine to make to exchange to the cationic stabilized in molecular sieve.
4, treated after the ion exchange with catalytic activity and drying and calcining, molecular sieve disperses in water, then mixes It is incorporated into a certain proportion of hollow alumina bead powder, the matter when molecular sieve is mixed with the hollow alumina bead powder Amount ratio is from 2:1, boehmite and hydroxyethyl cellulose is added after fully dispersed, cordierite honeycomb is coated to after stirring evenly On carrier, the catalyst coat of tens microns of thickness is formed in the tiny cell walls of honeycomb substrate.
Embodiment 2
The present embodiment is substantially the same manner as Example 1, differs only in:The molecular sieve is Cu-ZSM-5 molecular sieves In.
Embodiment 3
The present embodiment is substantially the same manner as Example 1, differs only in:The molecular sieve is Beta molecular sieves.
The performance test results for the molecular sieve carried catalyst that embodiment 1-3 is prepared are as shown in table 1 below:
Table 1
Reaction velocity is 90000 (h-1), 800ppmNH3, 800ppmNO, 8%O2,
By table 1 as it can be seen that the catalyst that embodiment 1 is prepared can be under conditions of broader temperature range and high-speed With high NOx conversion efficiency.
Embodiment 4
The present embodiment is substantially the same manner as Example 1, differs only in:The ZSM-35 molecular sieve and the hollow oxygen Mass ratio when changing the mixing of aluminium bead powder is 4:1.
Embodiment 5
The present embodiment is substantially the same manner as Example 1, differs only in:The ZSM-35 molecular sieve and the hollow oxygen Mass ratio when changing the mixing of aluminium bead powder is 8:1.
Embodiment 6
The present embodiment is substantially the same manner as Example 1, differs only in:The ZSM-35 molecular sieve and the hollow oxygen Mass ratio when changing the mixing of aluminium bead powder is 10:1.
Embodiment 7
The present embodiment is substantially the same manner as Example 1, differs only in:The ZSM-35 molecular sieve and the hollow oxygen Mass ratio when changing the mixing of aluminium bead powder is 12:1.
Embodiment 8
The present embodiment is substantially the same manner as Example 1, differs only in:The ZSM-35 molecular sieve and the hollow oxygen Mass ratio when changing the mixing of aluminium bead powder is 15:1.
The performance test results for the molecular sieve carried catalyst that embodiment 4-8 is prepared are as shown in table 2 below:
Table 2
Reaction velocity is 90000 (h-1), 800ppmNH3, 800ppmNO, 8%O2,
By table 2, it is seen then that mass ratio when ZSM-35 molecular sieve is mixed with the hollow alumina bead powder is to catalysis Agent performance has significant impact.And the mixing quality of ZSM-35 molecular sieve and the hollow alumina bead powder is 8:When 1, Conversion rate of NOx (%) under the conditions of 150~550 DEG C is above 70, and the conversion ratio is significantly higher than other ratio mixing Embodiment.
As described above, the present invention can be realized preferably.

Claims (9)

1. the preparation method of the catalyst for ammine selectivity catalytic reduction removing NOx, which is characterized in that include following step successively Suddenly:
(1) make molecular sieve carry out cation with the salting liquid of one or more kinds of metal cations by ion-exchange to exchange;
(2) after cation exchanges, the molecular sieve is washed with deionized, then dry at 50~200 DEG C, then 200~ 600 DEG C of temperature lower calcinations combine to make to exchange to the cationic stabilized in molecular sieve;
(3) the step (2), treated that molecular sieve disperses in water, remixes into a certain proportion of hollow alumina bead Powder, the mass ratio of the molecular sieve and the hollow alumina bead powder is from 2:1 to 15:1, it is added after fully dispersed viscous Mixture and thickener, are then applied on cordierite honeycomb carrier, and thickness tens is formed in the tiny cell walls of honeycomb substrate The catalyst coat of micron.
2. the preparation method for the catalyst of ammine selectivity catalytic reduction removing NOx, feature exist as described in claim 1 In in the step (1), the metal cation is copper ion, iron ion, titanium ion, vanadium ion and rare earth metal cations In it is one or more;The salting liquid is chloride, acetate, nitrate, sulfate or other halide.
3. the preparation method for the catalyst of ammine selectivity catalytic reduction removing NOx, feature exist as described in claim 1 In in the step (1), metal cation and the molecular sieve ratio of exchange are from 0.5% to 40%.
4. the preparation method for the catalyst of ammine selectivity catalytic reduction removing NOx, feature exist as described in claim 1 In further including following steps before the step (1):By molecular sieve precalcining.
5. the preparation method for the catalyst of ammine selectivity catalytic reduction removing NOx as described in claim 1, the step (2) in, dry drying time is 2~5 hours at described 50~200 DEG C;The calcining of 200~600 DEG C of temperature lower calcinations Time is 2~8 hours.
6. the preparation method for the catalyst of ammine selectivity catalytic reduction removing NOx, feature exist as described in claim 1 In the molecular sieve is ZSM-35 molecular sieve.
7. the preparation method for the catalyst of ammine selectivity catalytic reduction removing NOx, feature exist as described in claim 1 In the molecular sieve is one or both of ZSM-35 molecular sieve and Titanium Sieve Molecular Sieve.
8. the preparation method for the catalyst of ammine selectivity catalytic reduction removing NOx, feature exist as described in claim 1 In the molecular sieve is any one in ZSM-22 molecular sieves, Cu-ZSM-5 molecular sieves, Beta molecular sieves.
9. the catalyst for ammine selectivity catalytic reduction removing NOx, which is characterized in that use claim 1-8 any one The method is prepared.
CN201610292200.8A 2016-05-04 2016-05-04 Catalyst for removing NOx by ammonia selective catalytic reduction and preparation method thereof Active CN105772098B (en)

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WO2019104654A1 (en) * 2017-11-30 2019-06-06 中国科学院大连化学物理研究所 Denitration catalyst, preparation method therefor and application thereof in exhaust or waste gas denitration
CN114632537A (en) * 2022-03-29 2022-06-17 中国科学院城市环境研究所 Integral denitration catalyst and preparation method and application thereof

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US4260524A (en) * 1979-05-24 1981-04-07 Sumitomo Aluminium Smelting Company, Limited Hollow catalyst carrier and hollow catalyst made of transition-alumina and process for production thereof
CN1733361A (en) * 2004-08-13 2006-02-15 康捷环保科技股份有限公司 Denitrified catalyst for dissociating nitric oxide without reducing agent
US10632423B2 (en) * 2008-11-03 2020-04-28 Basf Corporation Bimetallic catalysts for selective ammonia oxidation
CN104368380A (en) * 2014-10-08 2015-02-25 宁波高新区永石科技有限公司 Catalyst for catalytic reduction denitration of diesel vehicle tail gas and preparation method thereof

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Patentee before: NINGBO FUKAI PURIFIER CO., LTD.