CN106794447A - Catalyst with improved hydrothermal stability - Google Patents

Catalyst with improved hydrothermal stability Download PDF

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Publication number
CN106794447A
CN106794447A CN201580045670.8A CN201580045670A CN106794447A CN 106794447 A CN106794447 A CN 106794447A CN 201580045670 A CN201580045670 A CN 201580045670A CN 106794447 A CN106794447 A CN 106794447A
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catalyst
ceria
ceo
weight
oxide
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薛文梅
魏昕熠
M·希尔真多夫
P·伯克
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BASF SE
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BASF SE
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Priority claimed from US14/467,250 external-priority patent/US9611774B2/en
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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
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/10Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of rare earths
    • 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
    • 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
    • B01D53/9422Processes characterised by a specific catalyst for removing nitrogen oxides by NOx storage or reduction by cyclic switching between lean and rich exhaust gases (LNT, NSC, NSR)
    • 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
    • B01D53/944Simultaneously removing carbon monoxide, hydrocarbons or carbon making use of oxidation catalysts
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/63Platinum group metals with rare earths or actinides
    • B01J35/30
    • B01J35/612
    • B01J35/613
    • B01J35/615
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/08Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
    • F01N3/10Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
    • F01N3/18Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control
    • F01N3/20Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control specially adapted for catalytic conversion ; Methods of operation or control of catalytic converters
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/204Alkaline earth metals
    • B01D2255/2042Barium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/206Rare earth metals
    • B01D2255/2065Cerium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/209Other metals
    • B01D2255/2092Aluminium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/90Physical characteristics of catalysts
    • B01D2255/91NOx-storage component incorporated in the catalyst
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/90Physical characteristics of catalysts
    • B01D2255/92Dimensions
    • B01D2255/9202Linear dimensions
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/90Physical characteristics of catalysts
    • B01D2255/92Dimensions
    • B01D2255/9207Specific surface
    • 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
    • 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
    • B01D53/9445Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC]
    • B01D53/945Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC] characterised by a specific catalyst
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts
    • B01J35/40
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0201Impregnation
    • B01J37/0203Impregnation the impregnation liquid containing organic compounds
    • 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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  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Toxicology (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Exhaust Gas After Treatment (AREA)
  • Processes For Solid Components From Exhaust (AREA)

Abstract

Disclose the catalyst for processing exhaust emission.The catalyst can include the ceria aluminium oxide particles with the ceria phase existed by the compound weight percentage of about 20% to about 80% based on oxide, the alkaline earth metal component being supported on the ceria aluminium oxide particles, wherein CeO2With hydrothermally stable and with N2In 2%O2It is less than after aging 5 hours at 950 DEG C with 10% steamAverage crystallite granularity microcrystalline form exist.

Description

Catalyst with improved hydrothermal stability
Technical field
The present invention relates to exhaust emission control catalyst and its application method.The present invention relates more specifically to resistant to heat aging catalyst With the method using the material.The exhaust emission control catalyst can be used to process exhaust stream, especially be discharged by lean-combustion engine Those.
Background
The user that operates to of lean-combustion engine, such as diesel engine and gasoline engine provides excellent fuel economy simultaneously There is the low emission of gas phase hydrocarbon and carbon monoxide because they run under the conditions of lean fuel under air/fuel ratio high.In addition, bavin Oil machine is provided better than gasoline (spark point in its fuel economy, durability and its under the low speed in terms of the ability of generation high torque Fire) engine remarkable advantage.
But, from from the point of view of emission, diesel engine there is a problem of more serious than their spark ignition opponent.Due to Diesel exhaust gas is multiphase mixture, and emission problem is related to particulate matter (PM), nitrogen oxides (NOx), unburned hydrocarbon (HC) and an oxygen Change carbon (CO).
Nitrogen oxides (the NO from lean-combustion engine must be reducedx) discharge to meet Abgasgesetz standard.Traditional triple effect Conversion (TWC) automobile catalyst is applied to the row for eliminating the engine run under the conditions of equal or close to stoichiometric air-fuel ratio NO in gasx, carbon monoxide (CO) and hydrocarbon (HC) pollutant.Produce the definite air-fuel ratio of stoichiometric condition with carbon in fuel and The relative scale of hydrogen and become.14.65:1 air-fuel ratio (A/F) (air weight/weight of fuel) be with average formula be CHl.88 Hydrocarbon fuel, the corresponding stoichiometric proportion of burning of such as gasoline.Therefore represented the specific A/F ratios of given fuel using sign of lambda Divided by stoichiometry A/F than result, therefore λ=1 is stoichiometric mixture, λ>1 is lean combustion mixture, and λ<1 is fuel-rich Mixture.
Used as fuel economy measure, engine, the gasoline-fueled engine in particular for car etc. just sets Count into and run under lean burn conditions.Such alternate-engine is referred to as " lean-combustion engine ".That is, starting to such Air-fuel ratio in the ignition mixture of machine supply is maintained at more than stoichiometric proportion so that gained is vented the oxygen of " dilute ", the i.e. exhaust Content is of a relatively high.Although lean-combustion engine provides advanced fuel economy, their shortcoming is due in exhaust Oxygen excess, traditional TWC catalyst can not effectively reduce the NO from such enginexDischarge.Overcome the trial of this problem Including using NOxTrap.The exhaust of such engine passes through catalyst/NOxAdsorbent is processed, the catalyst/NOxAbsorption Agent stores NO during (oxygen-enriched) operation of lean-burnxAnd stored NO is discharged during fuel-rich (fuel-rich) runsx.It is fuel-rich (or Stoichiometry) operation during, the catalyst/NOxThe catalytic component of adsorbent promotes NOxBy NOx(including from NOxAdsorbent The NO of middle releasex) it is reduced into nitrogen with the reaction of HC, CO and/or hydrogen present in exhaust.
In reducing environment, lean-burn NOxTrap (LNT) is by promoting steam reforming reaction and the Water gas shift/WGS of hydrocarbon (WGS) reaction and priming reaction are providing H2As reducing agent eliminating NOx.Water gas shift reaction be wherein carbon monoxide with Vapor reacts the chemical reaction to form carbon dioxide and hydrogen.The presence catalysis WGS of the ceria in LNT reacts to change Enter LNT to SO2The tolerance and stabilization PGM of deactivation;Ceria in LNT also functions as NOxStorage component.
It has been reported that comprising being fixed to ceria (CeO2) on barium (BaCO3) NOxStorage material, and these NOxMaterial has shown improved thermal ageing property.But, ceria at high temperature hydrothermal aging when there is serious sintering. The sintering not only causes low temperature NOxStorage volume and WGS activity are reduced, and also result in BaCO3With PGM by body (bulk) CeO2Bag Envelope.Accordingly, it would be desirable to the catalyst containing ceria of hydrothermally stable.
General introduction
The embodiment of the first aspect of the present invention is related to a kind of catalyst.In the first embodiment, the catalyst Comprising the dioxy with the ceria phase existed by the particle weight percentage of about 20% to about 80% based on oxide Change cerium-aluminium oxide particles, the alkaline earth metal component being supported on the ceria-alumina particle, wherein CeO2With hydro-thermal Stablize and with N2In 2%O2It is less than after aging 5 hours at 950 DEG C with 10% steamAverage crystallite The microcrystalline form of degree is present.
In this second embodiment, the catalyst of the first embodiment is improved, wherein the alkaline earth metal component is included Barium component.
In the 3rd embodiment, the catalyst of the second embodiment is improved, wherein the barium component is selected from barium monoxide And barium carbonate.
In the 4th embodiment, the catalyst of the first to the 3rd embodiment is improved, wherein the ceria-oxygen Change the compound that aluminum particulate is ceria and aluminum oxide.
In the 5th embodiment, the catalyst of first to fourth embodiment is improved, it further includes and is supported on At least one platinum group metal selected from platinum, palladium, rhodium, iridium and its mixture on the ceria-alumina particle.
In a sixth embodiment, improve the catalyst of the 5th embodiment, wherein the platinum group metal be selected from platinum, Palladium, rhodium and its mixture.
In the 7th embodiment, the catalyst of the second to the 6th embodiment is improved, wherein the barium component is pressing The amount of the weight of weight % to 50 % of oxide meter about 0.5 is present.
In the 8th embodiment, the catalyst of the second to the 7th embodiment is improved, wherein the barium component is pressing The amount of the weight of weight % to 30 % of oxide meter about 5 is present.
In the 9th embodiment, the catalyst of the 4th embodiment, wherein CeO are improved2And Al2O3Compound contain There is the ceria of the amount based on the weight % of oxide meter about 30 to 80.
In the tenth embodiment, the catalyst of the 4th embodiment, wherein CeO are improved2And Al2O3Compound contain There is the ceria of the amount based on the weight % of oxide meter about 50 to 80.
In the 11st embodiment, the catalyst of the 5th or the 6th embodiment is improved, wherein the platinum group metal Substantially it is made up of platinum and palladium.
In the 12nd embodiment, the catalyst of the 5th or the 6th embodiment is improved, wherein the platinum group metal Substantially it is made up of platinum.
In the 13rd embodiment, the catalyst of the first to the 12nd embodiment is improved, wherein the catalyst Selected from three-way catalyst (TWC), diesel oxidation catalyst (DOC), gasoline engine particulate filter (GPF), lean-burn NOxTrap (LNT), integrated lean-burn NOxTrap-three-way catalyst (LNT-TWC) or ammoxidation (AMOx).
The second aspect of the present invention is related to a kind of system.In the 14th embodiment, system includes first to the 13rd The catalyst of embodiment and the lean-combustion engine swum over the catalyst.
In the 15th embodiment, the system for improving the 12nd embodiment, it further includes the second catalyst With optional particulate filter.
In the 16th embodiment, the system for improving the 13rd embodiment, wherein the second catalyst is selected from triple effect Catalyst (TWC), gasoline engine particulate filter (GPF), SCR (SCR), lean-burn NOxTrap (LNT), ammonia oxygen Change (AMOx), SCR (SCRoF) on the filter and combinations thereof.
Brief description
Fig. 1 is can be comprising containing according to a honeycomb type fire resisting base members for the washcoat composition of the catalyst of embodiment Perspective view;
Fig. 2 is the partial section amplified relative to Fig. 1 and intercepted along the plane parallel with the end face of the substrate of Fig. 1, its The zoomed-in view of one of the gas flow shown in display Fig. 1;
Fig. 3 is when fresh and in N2In 2%O2With in 10% steam at 950 DEG C after aging 5 hours by according to reality Apply the CeO that the XRD of example is measured2Crystallite granularity curve map;With
Fig. 4 is measured by the XRD according to embodiment after aging 8 hours at 850 DEG C in 10% steam/air CeO2Crystallite granularity curve map.
Describe in detail
Before several exemplaries of the invention are described, it is to be understood that the invention is not restricted to description below The construction of middle elaboration or the details of processing step.The present invention can have other embodiments and can be implemented and carried out in a variety of ways.
Embodiment of the invention, it has been found that, by barium component (such as BaCO3And/or BaO) it is incorporated to titanium dioxide Cerium-aluminum oxide (CeO2/Al2O3) in CeO2There is provided with huge static stabilization and thus to have and improved than conventional art Hydrothermal stability, NO higherxThe NO of trapping capacity and Geng GaoxThe catalyst material of conversion ratio.
In one or more embodiments, catalyst is comprising ceria-alumina particle and is supported on the dioxy Change cerium-aluminium oxide particles on alkaline earth metal component, the ceria-alumina particle have by based on oxide about The ceria phase that compound weight percentage in the range of 20% to about 80% is present.By the fresh and aging of XRD acquisitions The average CeO of sample2Crystallite granularity can be used as CeO2Hydrothermal stability is measured.Correspondingly, in one or more embodiments In, CeO2With hydrothermally stable and with N2In 2%O2It is less than after aging 5 hours at 950 DEG C with 10% steam Average crystallite granularity microcrystalline form exist.
On term used in the disclosure, there is provided following definition.
Term " catalyst " used herein or " catalyst material " or " catalysis material " refer to the material for promoting reaction.
Term " layer " used herein and " layering " refer to be supported on surface, such as the structure in substrate.At one or many In individual embodiment, catalyst of the invention is coated in substrate or base members as washcoat, with the forming layer in substrate.
Term " washcoat " used herein has its its ordinary meaning in the art, that is, be applied to sufficiently porous to permit Perhaps the support base material that the gas streams for processing are passed through, such as the catalysis material on honeycomb type supporting member or other materials is thin Adherent coating.As understood in this area, washcoat available from slurry form particle dispersion, slurry is applied in substrate, does It is dry and calcine providing porous washcoat.
Term " carrier " used herein refer to carry thereon other chemical compounds or element in lower high surface Material.Carrier particle have be more thanHole and distribution of pores wide.As defined herein, such metal oxide carrier is not Including molecular sieve, especially zeolite.In specific embodiments, it is possible to use high surface refractory metal oxide carriers, example Such as alumina supporting material, also referred to as " gamma-alumina " or " activated alumina ", it is typically exhibited more than 60 meters squared per grams (“m2/ g "), typically up to about 200 meters squared per grams or BET surface area higher.Such activated alumina is typically oxidation The mixture of the γ and δ phases of aluminium, but it is also possible to η, κ and θ the oxidation aluminium phase containing significant quantity.Can be using beyond activated alumina Refractory metal oxides as at least some catalyst components in given catalyst carrier.For example, Bulk cerium oxide, oxygen Change zirconium, alpha-aluminium oxide, silica, titanium dioxide and other materials and become known for this kind of purposes.
In one or more embodiments, catalyst includes ceria-alumina particle.Ceria-alumina Particle has ceria phase, and ceria is by the catalyst weight based on oxide in the range of about 20% to about 80% Amount percentage is present, including 20%, 25%, 30%, 35%, 40%, 45%, 50%, 55%, 60%, 65%, 70%, 75% Or 80%.In one or more specific embodiments, the average CeO of the fresh and aged samples obtained by XRD2Crystallite granularity Can be used as CeO2Hydrothermal stability is measured.Correspondingly, in one or more embodiments, CeO2With hydrothermally stable and have In N2In 2%O2It is less than after aging 5 hours at 950 DEG C with 10% steamAverage crystallite granularity crystallite shape Formula exist, the Average crystallite granularity include 160,155,150,140,130,120,110,10.0,90,80,70,60,50, 40th, 30,20,10 andIn a specific embodiment, ceria-alumina particle include by based on oxide The ceria phase that compound weight percentage in the range of about 30% to 80 weight % is present.It is very specific real at one Apply in scheme, ceria-alumina particle is included by the compound weight hundred of based on oxide about 50% to 80 weight % Divide the ceria phase than existing.
In one or more embodiments, CeO2With hydrothermally stable and at 950 DEG C it is aging it is rear it is resistance to grow into it is bigger micro- Brilliant microcrystalline form is present.It is no more than average that term " resistance to growth " used herein refers to that crystallite grows to after weatheringGranularity.In a specific embodiment, in catalytic article in 2%O2With 10% steam/N2In it is old at 950 DEG C By the CeO of XRD determining after changing 5 hours2Crystallite granularity is less thanAccording to one or more embodiments, powder sample With the CeO of the catalyst of coating2Crystallite granularity is different.In the catalyst of coating, other washcoated layer components can be to CeO2With steady It is set for using.Therefore, after aging at same 950 DEG C, the CeO of the catalyst of the coating2Crystallite granularity is less than powder.
Term " Average crystallite granularity " used herein refers to the particle mean size such as by XRD determining as described below.
Term " XRD " used herein refers to X-ray diffraction crystallography, and it is the atomic and molecular structure for determining crystal Method.In XRD, crystallization atom makes x- beams towards many specific direction diffraction.By the angle for measuring these diffracted beams Degree and intensity, can produce the 3-D view of the electron density in crystal.By this electron density, it may be determined that the original in crystal Sub- position, and their chemical bond, their out-of-sequence and other information.Especially, XRD can be used to estimate crystallite granularity;Peak Width is inversely proportional with crystallite granularity;As crystallite granularity diminishes, peak broadens.In one or more embodiments, measured using XRD CeO2The Average crystallite granularity of particle.
The width at XRD peaks is interpreted to size and strains the combination of all related broadening effect.It is given below for surveying Both formula fixed.First equation is the crystallite granularity for full width at half maximum intensity FWHM information to be changed into given phase below Scherrer equations.Second equation is used to (be considered as such as the 3rd equation by the overall width or amplitude at peak width information and peak Shown in the two effects summation) calculate crystal in strain.It is noted that size and the broadening phase by different way of strain Change for Bragg angle θ.The constant of Scherrer equations is discussed below.
βe=C ε tan θ
The constant of Scherrer equations is
K:Shape constant, we use 0.9 value
L:Peak width, it is by using NIST SRM 660b LaB6 Line Position&Line Shape Standard To correct the influence from instrumental optics
Θ:The 1/2 of 2 θ values of associated reflections
λ:Radiation wavelength
" crystallite granularity " used herein is not understood as coherent scattering domain perpendicular to that group of lattice plane for producing reflection Length on direction.For CeO2, CeO2<111>Reflection is CeO2X-ray diffracting spectrum in highest peak.CeO2<111> Atomic plane intersect with each crystallographic axis at unity and perpendicular to<111>The body diagonal that vector is represented.Therefore, by CeO2111 reflections FWHM calculateCrystallite granularity be considered as substantially 100 layers<111>Atomic plane.
Different directions in crystal can produce different but close crystallite granularities with therefore reflection.Only it has been in crystal These values are just accurate when U.S. spherical.Consider total peak width by size and strain effect solution using Williamson Hall curve negotiatings Following linear equation is interpreted as, the slope of line represents strain, and intercept is crystal size.
In order to determine the crystallite granularity of material, single reflection or the FWHM values from complete X-ray diffracting spectrum are determined. Single reflection is traditionally fitted to determine the FWHM values of the reflection, for the influence correction FWHM values from instrument, has then been made The FWHM values of correction are converted into crystallite granularity with Scherrer equations.This passes through to ignore all from the strain in crystal Effect is realized.This method is mainly used in ask relevant with the crystallite granularity of noble metal (we only have single available reflection to it) Topic.It is noted that in peak is fitted, it is desirable to clean reflection not Chong Die with the reflection from other phases.Current is washcoated The fact that being formulated few, currently uses Rietveld methods.Rietveld methods can use the known crystalline substance of the phase for existing Body structure is fitted complete X-ray diffracting spectrum.Crystal structure serves as to the limitation of fit procedure or lock (brakes).For each Phase, changes phase content, lattice parameter and FWHM information until whole Model Matching experimental data.
In the following embodiments, the lab diagram of fresh and aged samples is simulated using Rietveld methods.Using to each Each FWHM curve determination crystallite granularities for mutually determining in sample.Do not include strain effect.
Term " alkaline-earth metal " used herein refers to one or more chemical element defined in the periodic table of elements, including Beryllium (Be), magnesium (Mg), calcium (Ca), strontium (Sr), barium (Ba) and radium (Ra).In one or more embodiments, alkaline-earth metal group Dividing can be used as salt and/or sulfate and/or oxide (such as BaCO3、BaSO4And/or BaO) be incorporated in catalyst to provide " alkali Earth metal component ".It is to be noted, that in calcining, barium component can change into barium carbonate and/or barium monoxide.In one or more implementations In scheme, alkaline earth metal component includes barium component.Alkaline earth metal component can be by based on oxide about 0.5 weights of weight % to 50 Amount %, including 0.5,1,2,3,4,5,10,15,20,25,30,35,40,45 and 50% amount is present in washcoat.At one In specific embodiment, alkaline earth metal component is included and deposited by the amount of based on the oxide about 0.5 weight % of weight % to about 50 Barium component.In other specific embodiments, alkaline earth metal component is included by based on oxide about 5 weight % to big The barium component that the amount of about 30 weight % is present.
In one or more embodiments, the CeO of the aged samples obtained by XRD is used2Crystallite granularity as alkaline earth/ Ce/Al hydrothermal stabilities are measured.
In a particular embodiment, when ceria-alumina particle barium precursor, particularly water-soluble barium precursor salt (such as barium acetate) (precursor salt provides barium carbonate (BaCO through calcining3) and/or barium monoxide (BaO)) dipping when, it was observed that huge Static stabilization.Reference picture 3, in N2In 2%O2With in 10% steam at 950 DEG C after aging 5 hours, BaCO3/ (CeO2-Al2O3) sample CeO2Crystallite granularity is about 75 to aboutIt is interior.This is significantly lower than aging BaCO3/CeO2 Powder ().In 70%CeO2/Al2O3Apply other BaCO on powder3Carrying capacity is determining whether they can also carry For similar effect.Reference picture 4, in 10% steam/air at 850 DEG C after aging 8 hours, is loaded with 15,10 and 5 weight % barium The sample of component (being calculated with barium monoxide) shows to compare BaCO3/CeO2Much lower CeO2Crystallite granularity.In general, barium component (such as BaCO3And/or BaO) seem there is unique stabilization to be turned into the ceric oxide crystallite growth in Ba/Ce/Al systems With.This static stabilization also benefits to the NO in such as LNT catalystxTrapping.From smaller crystallite granularity extra two Cerium oxide surface area realizes more low temperature ceria base NOxTrapping, improvement WGS and improvement PGM dispersions.
Therefore, according to one or more embodiments, ceria unstability in Ba-Ce systems is determined, and in Ba-Ce-Al Significantly stabilized in system.
In one or more embodiments, it is not intended to be subject to theory, it is believed that from smaller crystallite granularity extra two Cerium oxide surface area realizes BaCO higher3Base NOxTrapping (is attributed to more preferable BaCO3Dispersion), it is higher at low temperature CeO2Base NOxTrapping, improved NOxReduction (being attributed to more effective WGS) and improved NO oxidations and NOxReduction (is attributed to more Good PGM dispersions).Therefore, by barium (BaCO3And/or BaO) it is incorporated to ceria-alumina (CeO2/Al2O3) in CeO2Tool Having huge static stabilization and providing has hydrothermal stability more improved than conventional art, NO higherxTrapping capacity and more NO highxThe catalyst material of conversion ratio.
In one or more embodiments, in 2%O2With 10% steam/N2In at 950 DEG C after aging 5 hours, this hair Bright catalyst shows the improved NO in lean-burn runningxTrapping capacity and the improved NO in fuel-rich regenerative processxAlso It is former.The improvement be relative to comprising not with Al2O3With reference to ceria traditional catalyst.
In one or more embodiments, catalyst of the invention can be used as three-way catalyst (TWC), oxidative diesel Catalyst (DOC), gasoline engine particulate filter (GPF), lean-burn NOxTrap (LNT), integrated LNT-TWC or as ammoxidation Catalyst (AMOx).
In one or more embodiments, catalyst is further included and is supported on barium (ceria-alumina) particle On at least one platinum group metal.Term " platinum group metal " used herein or " PGM " refer to defined in the periodic table of elements Plant or various chemical elements, including platinum, palladium, rhodium, osmium, iridium and ruthenium and its mixture.In one or more embodiments, platinum family Metal is selected from platinum, palladium, rhodium, iridium and its mixture.In a specific embodiment, platinum group metal is selected from platinum, palladium, rhodium and its mixes Compound.Generally, the total platinum group metal content to involved catalyst is not specifically limited.
Generally, catalyst of the invention is arranged in substrate.Substrate can be commonly used for preparing those materials of catalyst Any materials of material, generally comprise ceramics or metal honeycomb structure.Any suitable substrate can be used, such as has to enter from substrate The monolith substrates of the type of mouth or exit face thin parallel gas flow channels therethrough, so that passage is opened flowing through fluid therein Put (herein referred to as flow through substrate).The essentially straight path of fluid issuing from their fluid intake to them Passage delimited by wall, catalysis material be coated on wall as washcoat so that the gas for flowing through passage contacts the catalysis material. The runner of monolith substrates is thin-walled channels, its can have any suitable section shape and size, such as trapezoidal, rectangle, square, Sine curve, hexagon, ellipse, circle etc..
Such monolith substrates can contain up to about 900 or more runner (or " hole ")/square inch sections, although Much less amount can be used.For example, substrate may have about 7 to 600, more typically about 100 to 400 holes/square Inch (" cpsi ").Hole can be with rectangle, square, circle, ellipse, triangle, hexagon or other polygonal section Face.Ceramic bases can be by any suitable refractory material, such as cordierite, cordierite-aluminum oxide, silicon nitride or carborundum system Into, or the substrate can be made up of one or more metal or metal alloy.
The catalyst of embodiment of the invention can be applied to substrate table by any any means known in this area On face.For example, catalyst wash coat can be by spraying, powder coated or brushing or by surface impregnation to the carbon monoxide-olefin polymeric Apply.
In one or more embodiments, catalyst is arranged in honeycomb substrates.
When applying as washcoat, the present invention is easier to understand with reference to Fig. 1 and 2.Figures 1 and 2 show that of the invention One fire resisting base members 2 of embodiment.Reference picture 1, fire resisting substrate unit 2 is with cylindrical outer surface 4, the and of upstream face 6 With the cylinder of the identical downstream end face 8 of end face 6.Base members 2 have the thin parallel gas flow channels 10 of the multiple for being formed wherein. As found out in Fig. 2, runner 10 is formed and from upstream face 6 to downstream end face 8 through substrate by wall 12, and passage 10 is unobstructed with permission Fluid, such as gas material flow longitudinally through substrate via gas channel 10.(it is in the art and under for single catalyst layer 14 Adhere in text sometimes referred to as " washcoat ") or be applied on the wall 12 of base members.In some embodiments, in catalyst Additional catalyst oxidant layer 16 is coated with layer 14.Second catalyst layer 16 can be constituted with the identical of catalyst layer 14, or second urges Agent layer 16 can include different carbon monoxide-olefin polymerics.
As shown in Figure 2, base members include the void space that is provided by gas channel 10, and these passages 10 section The thickness of area and the wall 12 for delimiting passage becomes with the type of base members.Similarly, it is applied to washcoated in such substrate The weight of layer optionally becomes.Therefore, when the amount of other components of washcoat or catalytic metal component or said composition is described, The use of the unit of the composition weight based on per unit volume substrate is convenient.Therefore, unit of gram/cubic feet per used herein Very little (" g/in3") and gram/cubic feet (" g/ft3") represent every volume base members (including the void space of base members Volume) composition weight.
In the second aspect of the invention, the catalyst of one or more of embodiments can be used in comprising one Or in multiple integrated discharge treating systems for the additional components for processing exhaust emission.For example, discharge treating system Can be included in the lean-combustion engine of the catalyst upstream of one or more embodiments, and can further include the second catalyst and Optionally include particulate filter.In one or more embodiments, the second catalyst is selected from three-way catalyst (TWC), gasoline Machine particulate filter (GPF), SCR (SCR), lean-burn NOxTrap (LNT), ammoxidation (AMOx), filtering SCR (SCRoF) on device and combinations thereof.In one or more embodiments, particulate filter may be selected from gasoline engine particulate mistake Filter, soot filter or SCRoF.Particulate filter can be catalyzed for specific function.Catalyst can be located at particulate filter Upstream or downstream.
In one or more embodiments, discharge treating system can be included in the catalyst of one or more embodiments The lean-combustion engine of upstream, and can further include TWC.In one or more embodiments, discharge treating system can enter one Step includes SCR/LNT.
In a specific embodiment, particulate filter is the soot filter (CSF) of catalysis.CSF can be included with containing There is the base of the washcoat coating of one or more catalyst for the soot and/or oxidation exhaust stream emission of burn off trapping Bottom.In general, soot burnt catalyst can be any known catalysts for soot burnt.For example, CSF can use one Plant or various high surface refractory oxides (such as aluminum oxide, silica, silica alumina, zirconium oxide and zirconium oxide Aluminum oxide) and/or oxidation catalyst (such as ceria-zirconia) coating for burning unburned hydrocarbon and to a certain extent Burning particles thing.In one or more embodiments, soot burnt catalyst is urged comprising one or more noble metal (PM) The oxidation catalyst of agent (platinum, palladium and/or rhodium).
In general, it is possible to use any known filter substrate in this area, including such as honeycomb wall flow filters Device, winding or fiberfill fibers filter, open celled foam, sintered metal filter etc., are specifically exemplified by wall-flow filter.Can be used for The wall-flow type substrate of load C SF compositions has the multiple thin substantially parallel gas channel extended along the longitudinal axis of substrate.It is logical Often, each passage is closed in one end of base body, with the alternate channel closed in opposite end face.Such monolith substrates can contain Up to about 900 or more runner (or " hole ")/square inch sections, although much less amount can be used.For example, Substrate may have about 7 to 600, more typically about 100 to 400 hole/square inches (" cpsi ").Embodiment party of the invention Porous flow honeycomb filter used has a high regard for choosing to be catalyzed in case, i.e., the wall of described element have thereon or its be contained within it is a kind of or Various catalysis materials, described above is such CSF carbon monoxide-olefin polymerics.Catalysis material may be present in the only entrance of element wall On side, only outlet side, entrance and exit side, or wall can be made up of catalysis material wholly or in part in itself.In another embodiment party In case, the present invention may include to use one or more catalysis material washcoats and one on the entrance and/or exit wall of the element The combination of individual or multiple catalysis material washcoats.
The present invention is described referring now to the following example.Before several exemplaries of the invention are described, Understand, the invention is not restricted to the construction or the details of processing step that are proposed in description below.The present invention can have other to implement Scheme and can be implemented and carried out in a variety of ways.
Embodiment
The preparation of 1-catalyst of embodiment
CeO2-Al2O3Particle (1A to 5A) is impregnated to provide sample 1B to 5B with barium acetate solution, and they have as in table 1 Specified BaCO3/(CeO2-Al2O3) and BaCO3Content.The mixture dried at 110 DEG C and at 720 DEG C calcining it is 2 small When.
CeO2-Al2O3Particle (4A) is impregnated to provide 4C to 4E with barium acetate solution, and they have as indicated in table 1 BaCO3/(CeO2-Al2O3) and BaCO3Content.The mixture is dried at 110 DEG C and calcined 2 hours at 620 DEG C.
CeO2Particle (6A) is impregnated to provide 6B and 6C with barium acetate solution, and they have the BaCO as indicated in table 13/ CeO2And BaCO3Content.The mixture is dried at 110 DEG C and calcined 2 hours at 600 DEG C.
Reference picture 3, in N2In 2%O2With in 10% steam at 950 DEG C after aging 5 hours, BaCO3/(CeO2- Al2O3) sample 1B-5B CeO2Crystallite granularity 79 toIt is interior.
Reference picture 4, in atmosphere in 10% steam at 850 DEG C after aging 8 hours, BaCO3/(CeO2-Al2O3) sample The CeO of 4C to 4E2Crystallite granularity 73 toIt is interior.
The display of table 1 1A to 6A and 1B to 6B, 6C, the content of 4C to 4E.
Table 1
* aging condition:In N2In 2%O2With in 10% steam aging 5 hours at 950 DEG C
- the XRD of embodiment 2 is measured
The CeO of the sample of embodiment 1 is measured by XRD2Crystallite granularity.Use mortar and pestle sample.Gained powder Then it is backfilling into flat base (flat plate mounts) for analysis.Use θ-θ PANalytical X ' Pert Pro MPD X-ray diffractions system collects data in Bragg-Brentano geometry.Light path is by X-ray pipe, 0.04rad Soller slits, 1/4 ° of divergent slit, 15mm light beam masks, 1/2 ° of antiscatter slits, sample, 1/4 ° of antiscatter slits, 0.04rad soller slits, Ni ° of optical filter and with 2.114 ° of PIXcel linear position sensitive detector structures of effective length Into.In this analysis Cu is used in the case where the generator of 45kV and 40mA is setRadiation.Walk using 0.026 ° of stride and often 600s Gate time from 10 ° to 90 ° 2 θ collect X-ray diffraction data.The identification of phase is carried out using Jade softwares.All numerical value make Determined with Rietveld methods.
This specification mentions " embodiment ", " some embodiments ", " one or more embodiments " in the whole text Or " embodiment " refer to the specific factor of embodiment description, structure, material or feature are included in it is of the invention In at least one embodiment.Therefore, as " in one or more embodiments ", " in certain embodiments ", " at one In embodiment " or this specification appearance in the whole text everywhere that is expressed in of " in one embodiment " etc be not necessarily referring to this hair Bright same embodiment.Additionally, specific factor, structure, material or feature can be combined at one in any suitable manner Or in multiple embodiments.The description order of the above method is not construed as limitation, and method can using disengaging order or With deleting or the increased operation.
It is to be understood that description above mean it is exemplary and nonrestrictive.Many other embodiments are in this area Those of ordinary skill is readily apparent that after reading description above.Therefore, appended claims and these claims be should refer to The full breadth of equivalent determine the scope of the present invention.

Claims (15)

1. a kind of catalyst, it is included
Dioxy with the ceria phase existed by the particle weight percentage of about 20% to about 80% based on oxide Change cerium-aluminium oxide particles, the alkaline earth metal component being supported on the ceria-alumina particle, wherein CeO2With hydro-thermal Stablize and with N2In 2%O2It is less than after aging 5 hours at 950 DEG C with 10% steamAverage crystallite The microcrystalline form of degree is present.
2. the catalyst of claim 1, wherein the alkaline earth metal component includes barium component.
3. the catalyst of claim 2, wherein the barium component is selected from barium monoxide and barium carbonate.
4. the catalyst of any one of claim 1-3, wherein the ceria-alumina particle is ceria and aluminum oxide Compound.
5. the catalyst of any one of claim 1-4, it is further comprising being supported on the ceria-alumina particle Selected from least one platinum group metal of platinum, palladium, rhodium, iridium and its mixture.
6. the catalyst of claim 5, wherein the platinum group metal is selected from platinum, palladium, rhodium and its mixture.
7. the catalyst of claim 2, wherein the barium component is by the amount of based on oxide about 0.5 weight of weight % to 50 % In the presence of especially the barium component exists by the amount of based on oxide about 5 weight of weight % to 30 %.
8. the catalyst of claim 4, wherein CeO2And Al2O3Compound contain about 30 to the 80 weight % based on oxide Amount ceria.
9. the catalyst of claim 4, wherein CeO2And Al2O3Compound contain about 50 to the 80 weight % based on oxide Amount ceria.
10. the catalyst of claim 5 or 6, wherein the platinum group metal is made up of platinum and palladium substantially.
The catalyst of 11. claims 5 or 6, wherein the platinum group metal is made up of platinum substantially.
The catalyst of 12. claim any one of 1-11, wherein the catalyst is selected from three-way catalyst (TWC), diesel engine oxygen Change catalyst (DOC), gasoline engine particulate filter (GPF), lean-burn NOxTrap (LNT), integrated lean-burn NOxTrap-triple effect Catalyst (LNT-TWC) or ammoxidation (AMOX).
A kind of 13. systems, its catalyst for including claim any one of 1-12 and the lean-burn swum over the catalyst start Machine.
The system of 14. claims 13, it further includes the second catalyst and optional particulate filter.
The system of 15. claims 14, wherein the second catalyst is selected from three-way catalyst (TWC), gasoline engine particulate filter (GPF), SCR (SCR), lean-burn NOxTrap (LNT), ammoxidation (AMOx), SCR on the filter (SCRoF) and combinations thereof.
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