CN104349839B - Scr catalyst and preparation method thereof - Google Patents

Scr catalyst and preparation method thereof Download PDF

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Publication number
CN104349839B
CN104349839B CN201280073796.2A CN201280073796A CN104349839B CN 104349839 B CN104349839 B CN 104349839B CN 201280073796 A CN201280073796 A CN 201280073796A CN 104349839 B CN104349839 B CN 104349839B
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China
Prior art keywords
scr catalyst
base material
catalyst composition
zeolite
ferrum
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CN201280073796.2A
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CN104349839A (en
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L·J·雷穆斯-耶格瑞斯
N·B·贾科布森
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Topsoe AS
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Haldor Topsoe AS
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Priority claimed from PCT/EP2012/066976 external-priority patent/WO2013182255A1/en
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Abstract

The present invention relates to a kind of NH3SCR catalyst and preparation method thereof, this NH3SCR catalyst includes that ferrum promotes β zeolite, cerium oxide and titanium dioxide, and optionally farther includes at least one in tungsten oxide, Dineodymium trioxide, silicon oxide and kieselguhr.

Description

SCR catalyst and preparation method thereof
The present invention relates to a kind of carbon monoxide-olefin polymeric (SCR) and the method preparing this SCR catalyst composition, described catalysis Agent compositions is for by reacting, with ammonia, the nitrogen oxides optionally reducing in waste gas.
Especially, the present invention provides NH3-SCR catalyst, it contains ferrum and promotes beta-zeolite, cerium oxide and titanium dioxide, and Comprise at least one in tungsten oxide, Dineodymium trioxide, silicon oxide and kieselguhr the most further.
SCR is for removing nitrogen oxides (NO from flue and waste gasx) it is well-known method.Many catalyst are at literary composition For at NO disclosed in offeringxReaction (DeNO with ammonia to nitrogenxActive catalyst in).
Known DeNOxThe problem of catalyst is that these catalyst have low activity under the high temperature higher than 500 DEG C.
Now, we have found a kind of particularly carbon monoxide-olefin polymeric, this carbon monoxide-olefin polymeric is in the temperature higher than 500 DEG C It is activity NH under degree3-SCR catalyst.
Thus, the present invention provides a kind of SCR catalyst composition, its comprise the ferrum being deposited on base material promote beta-zeolite, Cerium oxide and titanium dioxide.
Display further, as at least comprised in the composition in tungsten oxide, Dineodymium trioxide, silicon oxide and kieselguhr When planting, the catalysis activity of described catalyst can be further enhanced.
Certain form of flue gas contains substantial amounts of suspended solid, i.e. dust and flue dust, causes high corrosion tendency (erosion propensity)。
Have been found that adding kieselguhr in titanium dioxide obtains the repellence improving corrosion.
So, depend on application, in carbon monoxide-olefin polymeric, preferably comprise silicon with the diatomaceous amount of up to 60wt% Diatomaceous earth.
If not otherwise specified, all amounts that are above-mentioned and that hereinafter mention are calculated in weight percent, to comprise base material Carbon monoxide-olefin polymeric total amount calculate.
In embodiments of the invention, described carbon monoxide-olefin polymeric preferably further comprises tungsten oxide, Dineodymium trioxide, oxidation At least one in silicon and kieselguhr.
Base material preferably includes fibrous material and is configured to corrugated (corrugated shape).
In a preferred embodiment of the present invention, described carbon monoxide-olefin polymeric comprise 5 to 60wt% ferrum promote beta-zeolite, The cerium oxide of 2 to 20wt% and the titanium dioxide of 20 to 70wt%, and the WO of optional 2 to 6wt%3With 2 to 6wt%'s SiO2
In beta-zeolite the amount of ferrum preferably with the gauge of beta-zeolite between 0.5 to 15wt%.
Catalyst according to the invention compositions provides the High-temperature scr catalyst with long-time stability.
The compositions of the present invention has extensively at engine exhaust with in the denitrogenation of the waste gas of stationary source such as electric station General application.
In some application above-mentioned, it is preferable that described carbon monoxide-olefin polymeric is provided at en-block construction base material On (monolithic structured substrate).
Preferably fiber base material is bellows-shaped.
Described catalyst can also be provided at wall flow particulate filters (particulate wall flow Filter) in, such as in the waste gas cleaning system of compression ignition engine.
The present invention further provides the preparation method of SCR catalyst that is disclosed above and that limit, the method include with Lower step:
Base material is provided;
Thering is provided priming paint (wash coat), this priming paint comprises ferrum and promotes beta-zeolite and titanium dioxide, and wraps the most further Silicon oxide-containing and/or kieselguhr;
It is coated with cloth base material with described priming paint and is dried and calcines this base material being coated with priming paint;
Then, should with the aqueous impregnation containing cerium oxide precursor and optional tungsten oxide precursor and/or Dineodymium trioxide precursor The base material being coated with priming paint through calcining;And
Calcine this base material being through impregnation with, cerium oxide precursor to be converted into cerium oxide, and by optional tungsten oxide precursor And/or Dineodymium trioxide precursor is converted into tungsten oxide and/or Dineodymium trioxide.
Preferably, described priming paint comprise with the total amount of priming paint and base material be calculated as 5 to 60wt% ferrum promote beta-zeolite, 2 to The cerium oxide of 20wt% and the titanium dioxide of 20 to 70wt%.
If any, it is preferable that in carbon monoxide-olefin polymeric in terms of the total amount of priming paint and base material the amount of tungsten oxide be 2 to 6wt%, the amount of silicon oxide are 2 to 6wt% and diatomaceous amount is 0 to 60%.
In beta-zeolite, the amount of ferrum accelerator is preferably 0.5 to 15wt% with the gauge of beta-zeolite.
In embodiments of the invention, base material includes fibrous material, is preferably made up of glass fibre or ceramic fibre.
Embodiment
Embodiment 1
According to one embodiment of the invention, the preparation of catalyst comprises the steps of:
Corrugated fibrous glass base material is provided;
Thering is provided priming paint, by the ferrum of 30%, described priming paint promotes that the titanium dioxide of beta-zeolite and 40wt% forms, described ferrum promotees Enter the ferrum that beta-zeolite comprises 0.5wt%;
Described component is mixed with butanol;
It is coated with cloth base material with priming paint and is dried and calcines this base material being coated with priming paint;
Then, with the aqueous solution containing the cerous nitrate as cerium oxide precursor at 550 DEG C, impregnate this coating through calcining There is the base material of priming paint;
This base material being through impregnation with is calcined, cerium oxide precursor to be changed into cerium oxide, and in the catalysis made at 450 DEG C Agent reaches the cerium oxide of 10wt%.
Embodiment 2
Catalyst test
The present embodiment is given following catalyst at 550 DEG C through time activity level comparison:
1) reference Fe β/TiO2Catalyst.
2) reference Fe β/TiO2Catalyst+5%CeO2
3) reference Fe β/TiO2Catalyst+10%CeO2
4) reference Fe β/TiO2Catalyst+20%CeO2
5) reference Fe β/TiO2Catalyst+10%CeO2And 10%Nd2O3
6) reference Fe β/TiO2Catalyst+5%CeO2, 4%WO3And 4%SiO2
In laboratory reactor, test catalyst, use the sample cut from monolithic sample (monolith sample) Product plate (plates), and by sample panel alignment (aligned) so that gas is along sample panel Surface runoff.Reactor is mounted with 4 Block sample panel (long 3.5cm, wide 1.1cm, thick 0.8mm).Inlet gas comprises 5%H2O, 4%O2And N2As surplus.Entrance NO concentration is 500ppm and entrance NH3/ NO ratio is 1.5.Temperature is 550 DEG C and equivalent airspeed (EAS) (equivalent GHSV) For 72000Nm3/m3/h.The air-flow of unit catalyst weight is 80Nm3/h/kg。
Activity coefficient (activity coefficient) is calculated as below:
KNOx=-NHSV*ln (1-NO conversion).
The characteristic of catalyst 1-6 listed above is summarized in Fig. 1 of accompanying drawing.

Claims (6)

1. a SCR catalyst composition, it is deposited on base material, and described SCR catalyst composition comprises and combines with catalyst The total amount meter of thing and base material,
The ferrum of 5 to 60wt% promotes beta-zeolite,
The titanium dioxide of 20 to 70wt%,
The cerium oxide of 2 to 20wt%,
The tungsten oxide of 2 to 6wt%,
The silicon oxide of 2 to 6wt%, and
The kieselguhr of 0 to 60wt%.
SCR catalyst composition the most according to claim 1, wherein said ferrum promotes that beta-zeolite comprises the amount with beta-zeolite It is calculated as the ferrum of 0.5 to 15wt%.
SCR catalyst composition the most according to claim 1 and 2, wherein said base material includes fibrous material.
SCR catalyst composition the most according to claim 3, wherein said fibrous material is by glass fibre or ceramic fibre Constitute.
SCR catalyst composition the most according to claim 1, is wherein configured to corrugated by described base material.
SCR catalyst composition the most according to claim 1, wherein said base material is wall flow particulate filters.
CN201280073796.2A 2012-06-06 2012-08-31 Scr catalyst and preparation method thereof Active CN104349839B (en)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
DKPA201270304 2012-06-06
DKPA201270304 2012-06-06
PCT/EP2012/066976 WO2013182255A1 (en) 2012-06-06 2012-08-31 Scr catalyst and method of preparation thereof

Publications (2)

Publication Number Publication Date
CN104349839A CN104349839A (en) 2015-02-11
CN104349839B true CN104349839B (en) 2016-11-30

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