EP4228810A1 - Adsorbeur d'oxyde d'azote passif - Google Patents

Adsorbeur d'oxyde d'azote passif

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Publication number
EP4228810A1
EP4228810A1 EP21786991.6A EP21786991A EP4228810A1 EP 4228810 A1 EP4228810 A1 EP 4228810A1 EP 21786991 A EP21786991 A EP 21786991A EP 4228810 A1 EP4228810 A1 EP 4228810A1
Authority
EP
European Patent Office
Prior art keywords
palladium
zeolite
catalyst
cesium
catalyst according
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
EP21786991.6A
Other languages
German (de)
English (en)
Inventor
Hannelore GEERTS-CLAES
Christoph Hengst
Frank-Walter Schuetze
Johan Adriaan Martens
Michiel DE PRINS
Sam Smet
Gina Vanbutsele
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Umicore AG and Co KG
Original Assignee
Umicore AG and Co KG
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Umicore AG and Co KG filed Critical Umicore AG and Co KG
Publication of EP4228810A1 publication Critical patent/EP4228810A1/fr
Pending legal-status Critical Current

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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
    • 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
    • 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
    • B01D53/02Separation 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 by adsorption, e.g. preparative gas chromatography
    • 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
    • B01D53/9459Removing one or more of nitrogen oxides, carbon monoxide, or hydrocarbons by multiple successive catalytic functions; systems with more than one different function, e.g. zone coated catalysts
    • B01D53/9477Removing one or more of nitrogen oxides, carbon monoxide, or hydrocarbons by multiple successive catalytic functions; systems with more than one different function, e.g. zone coated catalysts with catalysts positioned on separate bricks, e.g. exhaust systems
    • 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
    • B01D53/9481Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start
    • 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
    • B01J23/40Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals of the platinum group metals
    • B01J23/44Palladium
    • 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
    • B01J23/58Platinum group metals with alkali- or alkaline earth metals
    • BPERFORMING OPERATIONS; TRANSPORTING
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    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/70Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of types characterised by their specific structure not provided for in groups B01J29/08 - B01J29/65
    • B01J29/72Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of types characterised by their specific structure not provided for in groups B01J29/08 - B01J29/65 containing iron group metals, noble metals or copper
    • B01J29/74Noble metals
    • BPERFORMING OPERATIONS; TRANSPORTING
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    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/82Phosphates
    • 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
    • B01J35/19Catalysts containing parts with different compositions
    • BPERFORMING OPERATIONS; TRANSPORTING
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    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
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    • B01J37/02Impregnation, coating or precipitation
    • B01J37/024Multiple impregnation or coating
    • B01J37/0244Coatings comprising several layers
    • BPERFORMING OPERATIONS; TRANSPORTING
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    • B01J37/02Impregnation, coating or precipitation
    • B01J37/024Multiple impregnation or coating
    • B01J37/0246Coatings comprising a zeolite
    • 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
    • F01N3/02Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust
    • F01N3/021Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters
    • F01N3/033Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters in combination with other devices
    • F01N3/035Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters in combination with other devices with catalytic reactors, e.g. catalysed diesel particulate filters
    • 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
    • F01N3/0807Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
    • F01N3/0814Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents combined with catalytic converters, e.g. NOx absorption/storage reduction catalysts
    • 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
    • F01N3/0807Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
    • F01N3/0828Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents characterised by the absorbed or adsorbed substances
    • F01N3/0842Nitrogen oxides
    • 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
    • F01N3/2066Selective catalytic reduction [SCR]
    • 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
    • F01N3/24Exhaust 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 constructional aspects of converting apparatus
    • F01N3/28Construction of catalytic reactors
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/106Silica or silicates
    • B01D2253/108Zeolites
    • B01D2253/1085Zeolites characterized by a silicon-aluminium ratio
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/112Metals or metal compounds not provided for in B01D2253/104 or B01D2253/106
    • B01D2253/1122Metals
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/102Platinum group metals
    • B01D2255/1023Palladium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/50Zeolites
    • 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
    • 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
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2229/00Aspects of molecular sieve catalysts not covered by B01J29/00
    • B01J2229/10After treatment, characterised by the effect to be obtained
    • B01J2229/18After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself
    • B01J2229/186After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself not in framework positions
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2229/00Aspects of molecular sieve catalysts not covered by B01J29/00
    • B01J2229/30After treatment, characterised by the means used
    • B01J2229/42Addition of matrix or binder particles
    • 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
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • 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
    • F01N2510/00Surface coverings
    • F01N2510/06Surface coverings for exhaust purification, e.g. catalytic reaction
    • 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
    • F01N2510/00Surface coverings
    • F01N2510/06Surface coverings for exhaust purification, e.g. catalytic reaction
    • F01N2510/063Surface coverings for exhaust purification, e.g. catalytic reaction zeolites
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • 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

Definitions

  • the present invention relates to a passive nitrogen oxide adsorber for the passive storage of nitrogen oxides from the exhaust gas of a combustion engine, which comprises a zeolite of the structure type RHO containing palladium and cesium.
  • the exhaust gas of motor vehicles that are operated with lean-burn combustion engines contain carbon monoxide (CO) and nitrogen oxides (NOx), as well as components that result from the incomplete combustion of the fuel in the combustion chamber of the cylinder.
  • CO carbon monoxide
  • NOx nitrogen oxides
  • the latter are in particular residual hydrocarbons (HC) and particle emissions, also referred to as “diesel soot” or “soot particles”.
  • a known method for removing nitrogen oxides from exhaust gases in the presence of oxygen is selective catalytic reduction (SCR.) by means of ammonia on a suitable catalyst.
  • SCR selective catalytic reduction
  • the nitrogen oxides to be removed from the exhaust gas are converted to nitrogen and water using ammonia.
  • Iron-exchanged and, in particular, copper-exchanged zeolites, for example may be used as SCR catalysts; see, for example, W02008/106519 Al, WO2008/118434 Al, and WO2008/132452 A2.
  • SCR catalysts only work from an exhaust gas temperature of approx. 180 to 200 °C and do not, therefore, convert nitrogen oxides that are formed in the engine's cold-start phase.
  • nitrogen oxide storage catalysts are also known, for which the term, "Lean NOx Trap,” or LNT, is common. Their cleaning action is based upon the fact that in a lean operating phase of the engine, the nitrogen oxides are predominantly stored in the form of nitrates by the storage material (oxides, carbonates, or hydroxides of magnesium, calcium, strontium, barium, alkali metals, rare earth metals, or mixtures thereof) of the storage catalyst, and the nitrates are broken down again in a subsequent rich operating phase of the engine, and the nitrogen oxides which are thereby released are converted with the reducing exhaust gas components in the storage catalyst to nitrogen, carbon dioxide, and water.
  • This operating principle is described in, for example, SAE document SAE 950809.
  • SAE Technical Paper 950809 is also referred to as active nitrogen oxide storage.
  • nitrogen oxides may - particularly at temperatures below 200 °C, at which an SCR. catalyst has not yet reached its operating temperature - be stored and released again as soon as the SCR catalyst is ready for operation.
  • an increased total nitrogen oxide conversion is realized in the exhaust gas after-treatment system by the interim storage below 200 °C of the nitrogen oxides emitted by the engine, as well as the concerted release of those nitrogen oxides above 200 °C.
  • Palladium supported on cerium oxide has been described as a passive nitrogen oxide storage catalyst (see, for example, W02008/047170 Al and WO2014/184568 Al). From WO2012/166868 Al, it is known to use a zeolite as a passive nitrogen oxide storage catalyst, which zeolite contains, for example, palladium and a further metal, such as iron, for example.
  • W02015/085303 Al discloses passive nitrogen oxide storage catalysts which contain a precious metal and a small-pore molecular sieve with a maximum ring size of eight tetrahedral atoms.
  • a passive nitrogen oxide storage catalyst comprising a certain small-pore molecular sieve with a maximum ring size of eight tetrahedral atoms and palladium is also known from EP 3 449 999 Al.
  • WO2016/135465 Al discloses a passive NOx adsorber which comprises a first noble metal and a molecular sieve having a MAZ Framework Type.
  • the first noble metal can be palladium.
  • W02020/039015 Al discloses a passive NOx adsorber which comprises a carrier substrate, palladium and a zeolite which belongs to the structure type MOZ or ZSM-10.
  • US2016/279598 discloses a passive NOx adsorber which comprises a first noble metal and a molecular sieve having an OFF Framework Type. The first noble metal can be palladium.
  • Passive NOx absorbers are also disclosed in US2020/016571.
  • EP3334912B1 discloses an exhaust system for treating an exhaust gas which comprises (i) a NOx absorber catalyst, (ii) means for introducing hydrocarbons into the exhaust gas and (iii) a lean NOx trap.
  • the NOx absorber catalyst comprises a molecular sieve and a noble metal, wherein the noble metal is preferably palladium whereas the molecular sieve is preferably a small pore molecular sieve.
  • the document discloses a long list of small pore molecular sieves including the Framework Type RHO.
  • zeolites belonging to the structure type RHO which comprise palladium and cesium have excellent passive nitrogen oxide adsorber properties.
  • zeolites of the structure type RHO provide an optimum of storage capacity and performance/transience which is believed to be based on the combination of channels of eight rings (8MR), six rings (6R) and double-eight rings (D8R).
  • the present invention relates, therefore, to a catalyst comprising a carrier substrate of length L, palladium, cesium and a zeolite of the structure type RHO.
  • Zeolites are two- or three-dimensional structures, the smallest structures of which can be considered to be SiO4 and Al 04 tetra hedra. These tetrahedra come together to form larger structures, wherein two are connected each time via a common oxygen atom. Different-sized rings may be formed thereby - for example, rings of four, six, or even nine tetrahedrally-coordinated silicon or aluminum atoms.
  • the different types of zeolite are often defined via the largest ring size, because this size determines which guest molecules can penetrate the zeolite structure, and which not. It is customary to differentiate between large-pore zeolites with a maximum ring size of 12, mediumpore zeolites with a maximum ring size of 10, and small-pore zeolites with a maximum ring size of 8.
  • zeolites are grouped by the Structural Commission of the International Zeolite Association into structural types which are each provided with a three-letter code; see, for example, Atlas of Zeolite Framework Types, Elsevier, 5th edition, 2001.
  • the catalyst according to the invention comprises zeolites whose largest channels are formed by 8 tetrahedrally-coordinated atoms and which belong to the structural type RHO. Given the definition for zeolites according to their biggest pore aperture as described above, RHO is a small pore zeolite
  • Rho see Adv. Chem. Ser., 121, 106-115 (1973)
  • LZ-214 see US 4,503,023
  • Pahasapaite see Jb. Miner.
  • Preferred zeolites of the structure type RHO have a silica-to-alumina molar ratio (SAR) of 5 to 50.
  • Zeolites of the structure type RHO can be obtained via known methods, for example via the method described in Microporous Materials, Vol. 4, 231-238 (1995) and in Verified Synthesis Of Zeolitic Materials, edited by Harry Robson and Karl Pettertechnischrud, Elsevier Science, 2001, pages 249-250.
  • the catalyst according to the present invention comprises palladium.
  • the palladium is preferably present thereby as palladium cation in the zeolite structure, i.e., in ion-exchanged form.
  • the palladium may also be wholly or partially present as palladium metal and/or as palladium oxide in the zeolite structure and/or on the surface of the zeolite structure.
  • palladium is preferably not present as part of the zeolite structure, i.e. palladium is preferably not part of the crystal lattice of the zeolite.
  • the palladium is present
  • the palladium may be present in quantities of 0.01 to 20 wt.% in relation to the sum of the weights of zeolite and palladium and calculated as palladium metal.
  • Palladium is preferably present in quantities of 0.5 to 10 wt.% - particularly preferably, of 0.5 to 4 wt.%, and, very particularly preferably, of 0.5 to 3 wt.% - in relation to the sum of the weights of zeolite and palladium and calculated as palladium metal.
  • the catalyst according to the present invention comprises cesium.
  • the cesium is preferably present thereby as cesium cation in the zeolite structure, i.e., in ion- exchanged form.
  • cesium is preferably not present as part of the zeolite structure, i.e. cesium is preferably not part of the crystal lattice of the zeolite.
  • the cesium may be present in quantities of 0.01 to 5 wt.% in relation to the sum of the weights of zeolite and cesium and calculated as cesium metal.
  • Cesium is preferably present in quantities of 0.1 to 4 wt.% - particularly preferably, of 0.3 to 3,5 wt.%, in relation to the sum of the weights of zeolite and cesium and calculated as cesium metal.
  • a particularly preferred catalyst of the present invention comprises a carrier substrate of length L, palladium in an amount of 0.5 to 4 wt.%, in relation to the sum of the weights of zeolite and palladium and calculated as palladium metal, cesium in an amount of 0.3 to 3,5 wt.%, in relation to the sum of the weights of zeolite and cesium and calculated as cesium metal and a zeolite of the structure type R.HO having a SAR. value of 5 to 50.
  • the catalyst according to the invention comprises a carrier substrate. This may be a flow-through substrate or a wall-flow filter.
  • a wall-flow filter is a carrier substrate that comprises channels of length L which extend in parallel between a first and a second end of the wall-flow filter, which are alternatingly sealed either at the first or second end, and which are separated by porous walls.
  • a flow-through substrate differs from a wall-flow filter, in particular, in that the channels of length L are open at its two ends.
  • wall-flow filters In an uncoated state, wall-flow filters have, for example, porosities of 30 to 80% - in particular, 50 to 75%. In the uncoated state, their average pore size is 5 to 30 micrometers, for example.
  • the pores of the wall-flow filter are so-called open pores, i.e., they have a connection to the channels. Furthermore, the pores are normally interconnected with one another. This enables easy coating of the inner pore surfaces, on the one hand, and an easy passage of the exhaust gas through the porous walls of the wall-flow filter, on the other hand.
  • Flow-through substrates are known to the person skilled in the art, as are wall-flow filters, and are commercially available. They consist, for example, of silicon carbide, aluminum titanate, or cordierite.
  • the catalyst according to the invention does not comprise any further metal except palladium and cesium - in particular, neither copper, nor iron, nor platinum.
  • the zeolite of the structure type RHO and the palladium and the cesium are present in the form of a coating on the carrier substrate.
  • the coating may thereby extend over the entire length L of the carrier substrate or only over a section thereof.
  • the coating may be situated on the surfaces of the input channels, on the surfaces of the output channels, and/or in the porous wall between the input and output channels.
  • Catalysts according to the present invention in which the zeolite of the structure type RHO, the palladium and the cesium are present in the form of a coating on the carrier substrate, may be produced according to the methods familiar to the person skilled in the art, such as according to the usual dip coating methods or pump and suck coating methods with subsequent thermal post-treatment (calcination).
  • a person skilled in the art knows that in the case of wall-flow filters, their average pore size and the average particle size of the materials to be coated can be adapted to each other such that they lie on the porous walls that form the channels of the wall-flow filter (on-wall coating).
  • the average particle sizes of the materials to be coated may, however, be selected such that said materials are located in the porous walls that form the channels of the wall-flow filter so that the inner pore surfaces are thus coated (in-wall coating).
  • the average particle size of the materials to be coated must be small enough to penetrate the pores of the wall-flow filter.
  • the zeolite of the structure type RHO, the palladium and the cesium are present coated over the entire length L of the carrier substrate, wherein no further catalytically active coating is found on the carrier substrate.
  • the carrier substrate may, however, also carry one or more further catalytically active coatings.
  • the carrier substrate may, in addition to a coating comprising the zeolite of the structure type RHO and the palladium, comprise a further coating which is oxidation-catalytically active.
  • the oxidation-catalytically-active coating comprises, for example, platinum, palladium, or platinum and palladium on a carrier material.
  • the mass ratio of platinum to palladium is, for example, 1 : 1 to 14: 1.
  • carrier materials All materials that are familiar to the person skilled in the art for this purpose are considered as carrier materials. They have a BET surface of 30 to 250 m 2 /g - preferably, of 100 to 200 m 2 /g (specified according to DIN 66132) - and are, in particular, aluminum oxide, silicon oxide, magnesium oxide, titanium oxide, and mixtures or mixed oxides of at least two of these materials.
  • Aluminum oxide, magnesium/aluminum mixed oxides, and aluminum/silicon mixed oxides are preferred.
  • the coating comprising the zeolite of the structure type RHO, the palladium and the cesium (hereinafter referred to as coating A) and the oxidation-catalytically- active coating (hereinafter referred to as coating B) may be arranged on the carrier substrate in various ways.
  • both coatings may, for example, be present coated over the entire length L or only over a section of the carrier substrate.
  • coating A starting from an end of the supporting body, may extend over 10 to 80% of its length L
  • coating B starting from another end of the supporting body, over 10 to 80% of its length LA.
  • L LA + LB applies, wherein LA is the length of the coating A, and LB is the length of the coating B.
  • L ⁇ LA + LB may also apply. In this case, coatings A and B overlap.
  • L > LA + LB may also apply if a section of the supporting body remains free of coatings. In the latter case, a gap remains between coatings A and B, which gap is at least 0.5 cm long, i.e., for example, 0.5 to 1 cm.
  • coatings A and B may both also be coated over the entire length L.
  • coating B for example, may be present directly on the carrier substrate, and coating A on coating B.
  • coating A may also be present directly on the carrier substrate, and coating B on coating A.
  • one coating extends over the entire length of the supporting body and the other over only a section thereof.
  • a zeolite of the structure type RHO comprises 0.5 to 4 wt.% of palladium, in relation to the sum of the weights of zeolite and palladium and calculated as palladium metal and cesium in an amount of 0.3 to 3,5 wt.%, in relation to the sum of the weights of zeolite and cesium and calculated as cesium metal, lies directly on the carrier substrate over its entire length L, and upon this coating is a coating containing platinum or platinum and palladium in a mass ratio of 1 : 1 to 14: 1, also over the entire length L.
  • the lower layer (Pd-Cs-RHO) is present thereby in a quantity of 50 to 250 g/L carrier substrate, and the upper layer (Pt or Pt/Pd) in a quantity of 50 to 150 g/L carrier substrate.
  • coatings A and B may extend over the entire length L of the wall-flow filter or over only a section thereof in a manner analogous to that described above for flow-through substrates.
  • the coatings may be on the walls of the input channels, on the walls of the output channels, or in the walls between the input and output channels.
  • the carrier substrate is formed from the zeolite of the structure type RHO, palladium, cesium and a matrix component.
  • Carrier substrates, flow-through substrates, and wall-flow substrates that do not just consist of inert material, such as cordierite, but additionally contain a catalytically active material are known to the person skilled in the art.
  • a mixture consisting of, for example, 10 to 95 wt.% of an inert matrix component and 5 to 90 wt.% of catalytically active material is extruded according to a method known per se.
  • All of the inert materials that are also otherwise used to produce catalyst substrates can be used as matrix components in this case. These are, for example, silicates, oxides, nitrides, or carbides, wherein magnesium aluminum silicates, in particular, are preferred.
  • the extruded carrier substrate which comprises the zeolite of the structure type RHO, as well as palladium and cesium, may be coated with one or more catalytically-active coatings, e.g., with the oxidation-catalytically-active coatings described above.
  • a carrier substrate which is composed of corrugated sheets of inert material.
  • carrier substrates are known to those skilled in the art as corrugated substrates.
  • Suitable inert materials are, for example, fibrous materials having an average fiber diameter of 50 to 250 m and an average fiber length of 2 to 30 mm.
  • fibrous materials are heat-resistant and consist of silicon dioxide, in particular of glass fibers.
  • sheets of said fiber materials are corrugated in a known manner and the individual corrugated sheets are formed into a cylindrical monolithically structured body with channels passing through the body.
  • a monolithic structured body having a criss-cross corrugation structure is formed.
  • non-corrugated, i.e. flat leaves can be arranged between the corrugated sheets.
  • Substrates composed of corrugated sheets may be directly coated with the catalyst of the present invention. It is however preferred to coat such substrates with an inert material, for example titania, first and only thereafter with the catalyst of the present invention.
  • an inert material for example titania
  • the catalyst according to the invention is especially suitable as a passive nitrogen oxide storage catalyst, i.e., it is able to store nitrogen oxides at temperatures below 200 °C and to release them again at temperatures above 200 °C. It is, therefore, possible, in combination with a downstream SCR. catalyst, to effectively convert nitrogen oxides across the entire temperature range of the exhaust gas, including the cold-start temperatures.
  • the present invention therefore relates to an exhaust gas system comprising a) a catalyst comprising a carrier substrate of length L, palladium, cesium, and a zeolite of the structure type RHO and b) an SCR catalyst.
  • the SCR catalyst in the exhaust gas system according to the invention may be selected from all the active catalysts in the SCR reaction of nitrogen oxides with ammonia - particularly such as are commonly known to the person skilled in the art in the field of automotive exhaust gas catalysis.
  • SCR catalysts are used that contain a smallpore zeolite with a maximum ring size of eight tetrahedral atoms and a transition metal.
  • SCR catalysts are described in, for example, W02008/106519 Al, WO2008/118434 Al, and WO2008/132452 A2.
  • large-pore and medium-pore zeolites may also be used, wherein those of the BEA structural type, in particular, come into question.
  • iron-BEA and copper-BEA are of interest.
  • zeolites belong to the BEA, AEI, AFX, CHA, KFI, ERI, LEV, MER, or DDR structure types and are particularly preferably exchanged with cobalt, manganese, iron, copper, or mixtures of two or three of these metals.
  • zeolites here also includes molecular sieves, which are sometimes also referred to as "zeolite- 1 ike" compounds. Molecular sieves are preferred, if they belong to one of the aforementioned structure types. Examples include silica aluminum phosphate zeolites, which are known by the term, SAPO, and aluminum phosphate zeolites, which are known by the term, AIPO.
  • Preferred zeolites are also those that have an SAR (silica-to-alumina molar ratio) value of 2 to 100, more preferably 5 to 50, and most preferably, the SAR. value is between 10 and 40.
  • SAR silicon-to-alumina molar ratio
  • the zeolites or molecular sieves contain transition metal - in particular, in quantities of 1 to 10 wt.%, and especially 2 to 5 wt.% - calculated as metal oxide, i.e., for example, as FezCh or CuO.
  • Preferred embodiments of the present invention contain beta-type (BEA), chabazite-type (CHA), AEI or Levyne-type (LEV) zeolites or molecular sieves exchanged with copper, iron, or copper and iron as SCR catalysts.
  • Appropriate zeolites or molecular sieves are known, for example, by the names, ZSM-5, Beta, SSZ-13, SSZ-39, SSZ-62, Nu-3, ZK-20, LZ-132, SAPO-34, SAPO-35, AIPO-34, and AIPO-35; see, for example, US 6,709,644 and US 8,617,474.
  • an injection device for reducing agent is located between the catalyst, which a carrier substrate of length L, palladium, and a zeolite whose largest channels are formed by 8 tetrahedrally-coordinated atoms, and the SCR catalyst.
  • the person skilled in the art may choose the injection device arbitrarily, wherein suitable devices may be found in the literature (see, for example, T. Mayer, Feststoff- SCR-System auf Basis von Ammoniumcarbamat (Solid SCR System Based upon Ammonium Carbamate), Dissertation, TU Kaiserslautern, 2005).
  • the ammonia as such or in the form of a compound may be introduced via the injection device into the exhaust gas flow from which ammonia is formed under the ambient conditions prevailing.
  • aqueous solutions of urea or ammonium formiate for example, come into consideration, such as solid ammonium carbamate.
  • the reducing agent or precursor thereof is held available in an accompanying container which is connected to the injection device.
  • the SCR. catalyst is preferably present in the form of a coating on a supporting body, which may be a flow-through substrate or a wall-flow filter and may, for example, consist of silicon carbide, aluminum titanate, or cordierite.
  • the supporting body itself may also consist of the SCR catalyst and a matrix component as described above, i.e., be present in extruded form.
  • the present invention also relates to a method for the cleaning of exhaust gases from motor vehicles that are operated by lean-burn engines, e.g., diesel engines, which method is characterized in that the exhaust gas is channeled through an exhaust gas system according to the invention.
  • lean-burn engines e.g., diesel engines
  • Example 1 a) 1.31 g of 18-crown-6, 1.80 g of CsOH (50%) and 0.44 g NaOH are mixed with 8.15 g of water. Upon obtaining a homogeneous solution, 1.92 g of Na-aluminate are added while stirring. The resulting mixture is stirred for another 15 minutes. Finally, 15.04 g of Ludox HS-40 is added dropwise while stirring. The resulting white gel is left stirring for 24 h before transferring it to a Teflon lined steel autoclave. The autoclave is placed in a preheated oven at 110 °C for 8 days. The product is recovered via filtration and washing until a pH of 10 is reached. b) The structure directing agent (SDA) is removed from the zeolite via a thermal treatment to 600 °C at a rate of 1 °C/min. The zeolite is kept at the maximum temperature for 8 h.
  • SDA structure directing agent
  • Figure 1 shows that a phase pure R.HO zeolite was formed.
  • the zeolite of the structure type R.HO comprising 3.2 wt.% of cesium as obtained according to the method described above is loaded with 2.4 wt.% of Pd via incipient wetness impregnation as follows: 116 pL of a 16.08 wt.% Pd solution is diluted with 92 pL water and dropwise added to 1 g of zeolite. The zeolite is thoroughly mixed after and dried at 60 °C overnight. The powder thus obtained is subsequently dried at 120 °C and hydrothermally treated at 550 °C.
  • the zeolite powder is pelletized as follows: the powder is placed between two stainless steel blocks and compressed at a pressure of 15 bar. The obtained pellet is crushed and sieved to obtain granulates sized 125 - 250 pm. These granulates are loaded in a quartz tube and exposed to a 20 mL/min airflow containing 12 vol% water. The temperature is raised with 5 °C/ min up to 750 °C. After 3 hours at 750°C the product is cooled in a 40 mL/min dry air flow.
  • the calcined powder containing Cs and Pd is suspended in demineralized water, mixed with 8% of a commercially available boehmite-based binder, and ground by means of a ball mill. Subsequently, according to a conventional method, a commercially available honeycomb ceramic substrate (flow-through substrate) is coated along its entire length with the washcoat thus obtained.
  • the washcoat load is 100 g/L in relation to the zeolite containing Cs and Pd (corresponds to 108 g/L incl. binder), which corresponds to a precious metal load of 68 g/ft 3 Pd.
  • the catalyst thus obtained is calcined at 550 °C.
  • a comparative example was prepared according to the preparation of Example 1, but using zeolite of type CHA instead of type R.HO.
  • the Cs- and Pd-loaded zeolite obtained in step e) of Example 1 is tested as follows: a) 300 mg of product is loaded in a quartz fixed bed tubular continuous flow reactor with online reaction product analysis. NO and NO2 concentrations were analyzed simultaneously on an ABB A02020-LimasllHW UV photometer. CO, N2O and CO2 were analyzed in parallel on an ABB A02020-URAS26 NDIR. photometer. Temperature was measured with a K type thermocouple inserted in the middle of the zeolite bed.
  • the test protocol entails four phases (figure 2): a pretreatment (phase (1)), a bypass (phase (2)), an isothermal adsorption (phase (3)) and a temperature programmed desorption (TPD) phase (phase (4)), see figure 2.
  • a pretreatment phase (1) the gas composition consists of 12 vol.-% O2 and 2.2 vol.-% H2O in N2 as a carrier gas. Temperature is increased with a ramp rate of 5°C/min to 500°C where it remains for 15 minutes. Then the sample is cooled down to 120 °C in the same feed gas. After the pretreatment the gas mixture is switched to bypass (2) and 160 vol. -ppm of NO and 800 vol.
  • the feed gas is switched from bypass to over the sample to measure the storage capacity in the adsorption phase (3).
  • the isothermal adsorption phase (3) at 120 °C lasts for 60 minutes during which the NOx after catalyst is measured and from which the NOx stored is calculated.
  • the temperature programmed desorption phase (4) begins and the temperature is gradually increased with 5 °C/min to 500 °C and remains for 5 minutes at 500 °C.
  • the gas hourly space velocity is fixed at 15,000 h ⁇ 1 , obtained by a gas flow rate of 167 mL/min over a catalyst bed of ca. 0.67 cm 3 .
  • Figure 3 shows the NOx adsorption data obtained.
  • the solid line shows the temperature adjusted in [°C], values given on the left axis of ordinate, the dashed line the NOx-concentration after the sample of Example 1, and the dotted line the NOx-concentration after the sample of Comparative Example 1 (for both concentrations values are also given on the left axis of ordinate, the unit is [vol.- PPm]).

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Abstract

La présente invention concerne un adsorbeur d'oxyde d'azote passif pour le stockage passif d'oxydes d'azote à partir des gaz d'échappement d'un moteur à combustion, qui comprend un substrat de support de longueur L, de césium, de palladium et une zéolite du type de structure RHO. Le catalyseur est utilisé dans un système de gaz d'échappement qui comprend un catalyseur SCR.
EP21786991.6A 2020-10-14 2021-10-14 Adsorbeur d'oxyde d'azote passif Pending EP4228810A1 (fr)

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US6709644B2 (en) 2001-08-30 2004-03-23 Chevron U.S.A. Inc. Small crystallite zeolite CHA
GB0620883D0 (en) 2006-10-20 2006-11-29 Johnson Matthey Plc Exhaust system for a lean-burn internal combustion engine
BRPI0808091A2 (pt) 2007-02-27 2014-07-15 Basf Catalysts Llc Catalisador, sistema de tratamento de gás de exaustão, processo para a redução de óxidos de nitrogênio, e, artigo de catalisador.
MY179762A (en) 2007-03-26 2020-11-12 Pq Corp Novel microporous crystalline material comprising a molecular sieve or zeolite having an 8-ring pore opening structure and methods of making and using same
EP3300791B1 (fr) 2007-04-26 2019-03-27 Johnson Matthey Public Limited Company Catalyseurs scr de zéolithe/métal de transition
US20090196812A1 (en) 2008-01-31 2009-08-06 Basf Catalysts Llc Catalysts, Systems and Methods Utilizing Non-Zeolitic Metal-Containing Molecular Sieves Having the CHA Crystal Structure
US20120308439A1 (en) 2011-06-01 2012-12-06 Johnson Matthey Public Limited Company Cold start catalyst and its use in exhaust systems
GB2514177A (en) 2013-05-17 2014-11-19 Johnson Matthey Plc Oxidation catalyst for a compression ignition engine
JP2017501329A (ja) 2013-12-06 2017-01-12 ジョンソン、マッセイ、パブリック、リミテッド、カンパニーJohnson Matthey Public Limited Company 貴金属及び小細孔モレキュラーシーブを含む受動的NOxアドソーバ
WO2016135465A1 (fr) 2015-02-26 2016-09-01 Johnson Matthey Public Limited Company Adsorbeur de nox passif
KR20170132158A (ko) 2015-03-25 2017-12-01 존슨 맛쎄이 퍼블릭 리미티드 컴파니 귀금속 및 OFF 프레임워크 유형을 갖는 분자체를 포함하는 수동 NOx 흡착제
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