CA2955817C - Catalyst with improved hydrothermal stability - Google Patents
Catalyst with improved hydrothermal stability Download PDFInfo
- Publication number
- CA2955817C CA2955817C CA2955817A CA2955817A CA2955817C CA 2955817 C CA2955817 C CA 2955817C CA 2955817 A CA2955817 A CA 2955817A CA 2955817 A CA2955817 A CA 2955817A CA 2955817 C CA2955817 C CA 2955817C
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- Prior art keywords
- catalyst
- ceria
- platinum
- barium
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- 239000003054 catalyst Substances 0.000 title claims abstract description 105
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 claims abstract description 67
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims abstract description 35
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 claims abstract description 25
- 230000032683 aging Effects 0.000 claims abstract description 18
- 229910052784 alkaline earth metal Inorganic materials 0.000 claims abstract description 11
- 150000001342 alkaline earth metals Chemical class 0.000 claims abstract description 11
- 239000002131 composite material Substances 0.000 claims abstract description 9
- AYJRCSIUFZENHW-UHFFFAOYSA-L barium carbonate Chemical compound [Ba+2].[O-]C([O-])=O AYJRCSIUFZENHW-UHFFFAOYSA-L 0.000 claims description 49
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical group [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims description 37
- 239000000203 mixture Substances 0.000 claims description 23
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims description 20
- 229910052788 barium Inorganic materials 0.000 claims description 19
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 claims description 19
- 229910052751 metal Inorganic materials 0.000 claims description 17
- 239000002184 metal Substances 0.000 claims description 17
- QVQLCTNNEUAWMS-UHFFFAOYSA-N barium oxide Chemical compound [Ba]=O QVQLCTNNEUAWMS-UHFFFAOYSA-N 0.000 claims description 15
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 12
- 230000003647 oxidation Effects 0.000 claims description 12
- 238000007254 oxidation reaction Methods 0.000 claims description 12
- 229910052697 platinum Inorganic materials 0.000 claims description 12
- 229910052763 palladium Inorganic materials 0.000 claims description 10
- 239000010948 rhodium Substances 0.000 claims description 8
- 229910052703 rhodium Inorganic materials 0.000 claims description 8
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims description 8
- 239000011246 composite particle Substances 0.000 claims description 7
- 238000011144 upstream manufacturing Methods 0.000 claims description 7
- 229910021529 ammonia Inorganic materials 0.000 claims description 6
- 229910052741 iridium Inorganic materials 0.000 claims description 4
- GKOZUEZYRPOHIO-UHFFFAOYSA-N iridium atom Chemical compound [Ir] GKOZUEZYRPOHIO-UHFFFAOYSA-N 0.000 claims description 4
- 238000010531 catalytic reduction reaction Methods 0.000 claims description 3
- 239000002245 particle Substances 0.000 abstract description 18
- 239000000758 substrate Substances 0.000 description 40
- 239000000463 material Substances 0.000 description 23
- 239000007789 gas Substances 0.000 description 19
- 239000000446 fuel Substances 0.000 description 16
- 230000000694 effects Effects 0.000 description 13
- 230000003197 catalytic effect Effects 0.000 description 12
- 238000006243 chemical reaction Methods 0.000 description 10
- 239000013078 crystal Substances 0.000 description 10
- 229930195733 hydrocarbon Natural products 0.000 description 9
- 150000002430 hydrocarbons Chemical class 0.000 description 9
- 238000000034 method Methods 0.000 description 9
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 7
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 description 7
- 229910002091 carbon monoxide Inorganic materials 0.000 description 7
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 6
- 238000002441 X-ray diffraction Methods 0.000 description 6
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 6
- 239000000843 powder Substances 0.000 description 6
- 239000004071 soot Substances 0.000 description 6
- 230000006641 stabilisation Effects 0.000 description 6
- 238000011105 stabilization Methods 0.000 description 6
- 238000003991 Rietveld refinement Methods 0.000 description 4
- ITHZDDVSAWDQPZ-UHFFFAOYSA-L barium acetate Chemical compound [Ba+2].CC([O-])=O.CC([O-])=O ITHZDDVSAWDQPZ-UHFFFAOYSA-L 0.000 description 4
- 238000002485 combustion reaction Methods 0.000 description 4
- 239000012530 fluid Substances 0.000 description 4
- 238000005259 measurement Methods 0.000 description 4
- 239000013618 particulate matter Substances 0.000 description 4
- 230000009467 reduction Effects 0.000 description 4
- 238000006722 reduction reaction Methods 0.000 description 4
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 239000006185 dispersion Substances 0.000 description 3
- 239000001257 hydrogen Substances 0.000 description 3
- 229910052739 hydrogen Inorganic materials 0.000 description 3
- 229910044991 metal oxide Inorganic materials 0.000 description 3
- 150000004706 metal oxides Chemical class 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 239000000377 silicon dioxide Substances 0.000 description 3
- 239000002594 sorbent Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 239000004215 Carbon black (E152) Substances 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- TZCXTZWJZNENPQ-UHFFFAOYSA-L barium sulfate Chemical compound [Ba+2].[O-]S([O-])(=O)=O TZCXTZWJZNENPQ-UHFFFAOYSA-L 0.000 description 2
- 239000011575 calcium Substances 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 229910052729 chemical element Inorganic materials 0.000 description 2
- 239000011248 coating agent Substances 0.000 description 2
- 238000000576 coating method Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000011777 magnesium Substances 0.000 description 2
- 230000000737 periodic effect Effects 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 239000010970 precious metal Substances 0.000 description 2
- 239000002243 precursor Substances 0.000 description 2
- 230000005855 radiation Effects 0.000 description 2
- 239000003870 refractory metal Substances 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 238000005245 sintering Methods 0.000 description 2
- -1 specifically Substances 0.000 description 2
- 238000003878 thermal aging Methods 0.000 description 2
- 239000011800 void material Substances 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 229910025794 LaB6 Inorganic materials 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- 101100238304 Mus musculus Morc1 gene Proteins 0.000 description 1
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 description 1
- 229910052581 Si3N4 Inorganic materials 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 238000007792 addition Methods 0.000 description 1
- 230000001464 adherent effect Effects 0.000 description 1
- 230000003679 aging effect Effects 0.000 description 1
- 229910052785 arsenic Inorganic materials 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910052790 beryllium Inorganic materials 0.000 description 1
- ATBAMAFKBVZNFJ-UHFFFAOYSA-N beryllium atom Chemical compound [Be] ATBAMAFKBVZNFJ-UHFFFAOYSA-N 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 230000001680 brushing effect Effects 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 230000001427 coherent effect Effects 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 229910052878 cordierite Inorganic materials 0.000 description 1
- 229910052593 corundum Inorganic materials 0.000 description 1
- 230000009849 deactivation Effects 0.000 description 1
- 238000002050 diffraction method Methods 0.000 description 1
- JSKIRARMQDRGJZ-UHFFFAOYSA-N dimagnesium dioxido-bis[(1-oxido-3-oxo-2,4,6,8,9-pentaoxa-1,3-disila-5,7-dialuminabicyclo[3.3.1]nonan-7-yl)oxy]silane Chemical compound [Mg++].[Mg++].[O-][Si]([O-])(O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2)O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2 JSKIRARMQDRGJZ-UHFFFAOYSA-N 0.000 description 1
- 238000007598 dipping method Methods 0.000 description 1
- 238000005538 encapsulation Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 238000009472 formulation Methods 0.000 description 1
- 239000008241 heterogeneous mixture Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 229910001092 metal group alloy Inorganic materials 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 239000002808 molecular sieve Substances 0.000 description 1
- 239000004570 mortar (masonry) Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 229910052762 osmium Inorganic materials 0.000 description 1
- SYQBFIAQOQZEGI-UHFFFAOYSA-N osmium atom Chemical compound [Os] SYQBFIAQOQZEGI-UHFFFAOYSA-N 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 229910052705 radium Inorganic materials 0.000 description 1
- HCWPIIXVSYCSAN-UHFFFAOYSA-N radium atom Chemical compound [Ra] HCWPIIXVSYCSAN-UHFFFAOYSA-N 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 229910052707 ruthenium Inorganic materials 0.000 description 1
- HBMJWWWQQXIZIP-UHFFFAOYSA-N silicon carbide Chemical compound [Si+]#[C-] HBMJWWWQQXIZIP-UHFFFAOYSA-N 0.000 description 1
- 229910010271 silicon carbide Inorganic materials 0.000 description 1
- HQVNEWCFYHHQES-UHFFFAOYSA-N silicon nitride Chemical compound N12[Si]34N5[Si]62N3[Si]51N64 HQVNEWCFYHHQES-UHFFFAOYSA-N 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 230000000087 stabilizing effect Effects 0.000 description 1
- 238000000629 steam reforming Methods 0.000 description 1
- 239000011232 storage material Substances 0.000 description 1
- 229910052712 strontium Inorganic materials 0.000 description 1
- CIOAGBVUUVVLOB-UHFFFAOYSA-N strontium atom Chemical compound [Sr] CIOAGBVUUVVLOB-UHFFFAOYSA-N 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 229910001845 yogo sapphire Inorganic materials 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/10—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of rare earths
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/38—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
- B01J23/54—Catalysts 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
- B01J23/56—Platinum group metals
- B01J23/63—Platinum group metals with rare earths or actinides
-
- B01J35/30—
-
- B01J35/612—
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- B01J35/613—
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- B01J35/615—
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/08—Heat treatment
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust 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
- F01N3/18—Exhaust 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
- F01N3/20—Exhaust 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/204—Alkaline earth metals
- B01D2255/2042—Barium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/206—Rare earth metals
- B01D2255/2065—Cerium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/209—Other metals
- B01D2255/2092—Aluminium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/90—Physical characteristics of catalysts
- B01D2255/91—NOx-storage component incorporated in the catalyst
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/90—Physical characteristics of catalysts
- B01D2255/92—Dimensions
- B01D2255/9202—Linear dimensions
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/90—Physical characteristics of catalysts
- B01D2255/92—Dimensions
- B01D2255/9207—Specific surface
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/01—Engine exhaust gases
- B01D2258/012—Diesel engines and lean burn gasoline engines
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9404—Removing only nitrogen compounds
- B01D53/9409—Nitrogen oxides
- B01D53/9413—Processes characterised by a specific catalyst
- B01D53/9422—Processes 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)
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/944—Simultaneously removing carbon monoxide, hydrocarbons or carbon making use of oxidation catalysts
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9445—Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC]
- B01D53/945—Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC] characterised by a specific catalyst
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2523/00—Constitutive chemical elements of heterogeneous catalysts
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- B01J35/40—
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/02—Impregnation, coating or precipitation
- B01J37/0201—Impregnation
- B01J37/0203—Impregnation the impregnation liquid containing organic compounds
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02T—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
- Y02T10/00—Road transport of goods or passengers
- Y02T10/10—Internal combustion engine [ICE] based vehicles
- Y02T10/12—Improving ICE efficiencies
Abstract
A catalyst for the treatment of exhaust gas emissions is disclosed. The catalyst can comprise ceria-alumina particles having a ceria phase present in a weight percent of the composite in the range of about 20% to about 80% on an oxide basis, an alkaline earth metal component supported on the ceria-alumina particles, wherein the Ce02 is present in the form of crystallites that are hydrothermally stable and have an average crystallite size less than 160 Å after aging at 950 °C for 5 hours in 2% 02 and 10% steam in N2.
Description
CATALYST WITH IMPROVED HYDROTHERMAL STABILITY
TECHNICAL FIELD
[0001] The present invention is directed to an exhaust gas purifying catalyst and methods .. for its use. More particularly, the invention pertains to catalysts that arc resistant to thermal aging and methods of using the materials. The exhaust gas purifying catalyst may be used to treat exhaust gas streams, especially those emanating from lean burn engines.
BACKGROUND
TECHNICAL FIELD
[0001] The present invention is directed to an exhaust gas purifying catalyst and methods .. for its use. More particularly, the invention pertains to catalysts that arc resistant to thermal aging and methods of using the materials. The exhaust gas purifying catalyst may be used to treat exhaust gas streams, especially those emanating from lean burn engines.
BACKGROUND
[0002] Operation of lean burn engines, for example, diesel engines and lean bum gasoline engines, provide the user with excellent fuel economy and have low emissions of gas phase hydrocarbons and carbon monoxide due to their operation at high air/fuel ratios under fuel lean conditions. Additionally, diesel engines offer significant advantages over gasoline (spark ignition) engines in terms of their fuel economy, durability, and their ability to generate high torque at low speed.
[0003] From the standpoint of emissions, however, diesel engines present more severe problems than their spark-ignition counterparts. Because diesel engine exhaust gas is a heterogeneous mixture, emission problems relate to particulate matter (PM), nitrogen oxides (NOR), unburned hydrocarbons (HC), and carbon monoxide (CO).
[0004] Emission of nitrogen oxides (NOR) from lean burn engines must be reduced in order to meet emission regulation standards. Conventional three-way conversion (TWC) automotive catalysts are suitable for abating NOR, carbon monoxide a (CO) and hydrocarbon (HC) pollutants in the exhaust of engines operated at or near stoichiometric air/fuel conditions. The precise proportion of air to fuel which results in stoichiometric conditions varies with the relative proportions of carbon and hydrogen in the fuel. An air-to-fuel (A/F) ratio of 14.65:1 (weight of air to weight of fuel) is the stoichiometric ratio corresponding to the combustion of a hydrocarbon fuel, such as gasoline, with an average formula CH1.88. The symbol X is thus used to represent the result of dividing a particular A/F ratio by the stoichiometric A/F ratio for a given fuel, so that; X=1 is a stoichiometric mixture, X>1 is a fuel-lean mixture and X,.<1 is a .. fuel-rich mixture.
[0005] Engines, especially gasoline-fueled engines to be used for passenger automobiles and the like, are being designed to operate under lean conditions as a fuel economy measure.
Such future engines are referred to as "lean burn engines." That is, the ratio of air to fuel in the combustion mixtures supplied to such engines is maintained above the stoichiometric ratio so that the resulting exhaust gases are "lean," i.e., the exhaust gases are relatively high in oxygen content. Although lean-burn engines provide advanced fuel economy, they have the disadvantage that conventional TWC catalysts are not effective for reducing NO.
emissions from such engines because of excessive oxygen in the exhaust.
Attempts to overcome this problem have included the use of a NO. trap. The exhaust of such engines is treated with a catalyst/NOr sorbent which stores NO. during periods of lean (oxygen-rich) operation, and releases the stored NO. during the rich (fuel-rich) periods of operation.
During periods of rich (or stoichiometric) operation, the catalyst component of the catalyst/NO. sorbent promotes the reduction of NO. to nitrogen by reaction of NO.
(including NO. released from the NO sorbent) with HC, CO, and/or hydrogen present in the exhaust.
Such future engines are referred to as "lean burn engines." That is, the ratio of air to fuel in the combustion mixtures supplied to such engines is maintained above the stoichiometric ratio so that the resulting exhaust gases are "lean," i.e., the exhaust gases are relatively high in oxygen content. Although lean-burn engines provide advanced fuel economy, they have the disadvantage that conventional TWC catalysts are not effective for reducing NO.
emissions from such engines because of excessive oxygen in the exhaust.
Attempts to overcome this problem have included the use of a NO. trap. The exhaust of such engines is treated with a catalyst/NOr sorbent which stores NO. during periods of lean (oxygen-rich) operation, and releases the stored NO. during the rich (fuel-rich) periods of operation.
During periods of rich (or stoichiometric) operation, the catalyst component of the catalyst/NO. sorbent promotes the reduction of NO. to nitrogen by reaction of NO.
(including NO. released from the NO sorbent) with HC, CO, and/or hydrogen present in the exhaust.
[0006] In a reducing environment, a lean NO. trap (LNT) activates reactions by promoting a steam reforming reaction of hydrocarbons and a water gas shift (WGS) reaction to provide H2 as a reductant to abate NOR. The water gas shift reaction is a chemical reaction in which carbon monoxide reacts with water vapor to form carbon dioxide and hydrogen.
The presence of ceria in an LNT catalyzes the WGS reaction, improving the LNTs resistance to SO2 deactivation and stabilizing the PGM; ceria in an LNT also functions as a NO. storage component.
The presence of ceria in an LNT catalyzes the WGS reaction, improving the LNTs resistance to SO2 deactivation and stabilizing the PGM; ceria in an LNT also functions as a NO. storage component.
[0007] NO, storage materials comprising barium (BaCO3) fixed to ceria (Ce02) have been reported, and these NO. materials have exhibited improved thermal aging properties.
Ceria, however, suffers from severe sintering upon hydrothermal aging at high temperatures.
The sintering not only causes a decrease in low temperature NO. storage capacity and WGS
activity, but also results in the encapsulation of BaCO3 and PGM by the bulk Ce02. Thus, there is a need for a ceria-containing catalyst that is hydrothermally stable.
SUMMARY
Ceria, however, suffers from severe sintering upon hydrothermal aging at high temperatures.
The sintering not only causes a decrease in low temperature NO. storage capacity and WGS
activity, but also results in the encapsulation of BaCO3 and PGM by the bulk Ce02. Thus, there is a need for a ceria-containing catalyst that is hydrothermally stable.
SUMMARY
[0008] Embodiments of a first aspect of the invention are directed to a catalyst. In a first embodiment, the catalyst comprises ceria-alumina composite particles having a ceria phase present in a weight percent of the composite in the range of 20 % to 80% on an oxide basis, an alkaline earth metal component comprising a barium component supported on the ceria-alumina composite particles and present in an amount in the range of 5.0 to 30% by weight on an oxide basis, wherein the Ce02 is present in the form of crystallites that are hydrothermally stable Date Regue/Date Received 2022-11-08 and have an average crystallite size as determined by XRD of less than 160A
after aging at 950 C for 5 hours in 2% 02 and 10% steam in N2
after aging at 950 C for 5 hours in 2% 02 and 10% steam in N2
[0009] In a second embodiment, the catalyst of the first embodiment is modified, wherein the barium component is selected from the group consisting of barium oxide and barium carbonate.
[0010] In a third embodiment, the catalyst of the first through second embodiments is modified, wherein the ceria-alumina particles are a composite of ceria and alumina.
[0011] In a fourth embodiment, the catalyst of the third embodiment is modified, wherein the composite of Ce02 and A1203 contains ceria in an amount in the range of about 30 to 80%
by weight on an oxide basis.
by weight on an oxide basis.
[0012] In a fifth embodiment, the catalyst of the third embodiment is modified, wherein the composite of Ce02 and A1203 contains ceria in an amount in the range of about 50 to 80%
by weight on an oxide basis.
by weight on an oxide basis.
[0013] In a sixth embodiment, the catalyst of the first through fifth embodiments further comprising at least one platinum group metal selected from the group consisting of platinum, palladium, rhodium, iridium, and mixtures thereof, supported on the ceria-alumina particles.
[0014] In a seventh embodiment, the catalyst of the sixth embodiment is modified, wherein the platinum group metal is selected from platinum, palladium, rhodium, and mixtures thereof.
[0015] In a eighth embodiment, the catalyst of the sixth through seventh embodiments is modified, wherein the platinum group metal consists essentially of platinum and palladium.
[0016] In the ninth embodiment, the catalyst of the sixth through seventh embodiments is modified, wherein the platinum group metal consists essentially of platinum.
[0017] In the tenth embodiment, the catalyst of the first through ninth embodiments is modified, wherein the barium component is present in an amount in the range of about 0.5%
to 50% by weight on an oxide basis.
to 50% by weight on an oxide basis.
[0018] In an eleventh embodiment, the catalyst of the first through tenth embodiments is modified, wherein the barium component is present in an amount in the range of about 5% to 30% by weight on an oxide basis.
[0019] In a twelfth embodiment, the catalyst of the first through eleventh embodiments is modified, wherein the catalyst is selected from a three-way catalyst (TWC), diesel oxidation catalyst (DOC), gasoline particulate filter (GPF), lean NO,, trap (LNT), integrated lean NOx trap-three way catalyst (LNT-TWC), or ammonia oxidation (AMOX).
Date Recue/Date Received 2022-05-20
Date Recue/Date Received 2022-05-20
[0020] A second aspect of the present invention is directed to a system.
In a thirteenth embodiment, a system comprises the catalyst of the first through twelfth embodiments and a lean burn engine upstream from the catalyst.
In a thirteenth embodiment, a system comprises the catalyst of the first through twelfth embodiments and a lean burn engine upstream from the catalyst.
[0021] In a fourteenth embodiment, the system of the thirteenth embodiment is modified, further comprising a second catalyst and,
[0022] In a fifteenth embodiment, the system of the thirteenth through fourteenth embodiments is modified further comprising a particulate filter.
[0023] In a sixteenth embodiment, the system of the fourteenth through fifteenth embodiments is modified, wherein the second catalyst is selected from a three-way catalyst (TWC), gasoline particulate filter (GPF), selective catalytic reduction (SCR), lean NO,, trap (LNT), ammonia oxidation (AMOX), SCR on a filter (SCRoF), and combinations thereof, and combinations thereof.
BRIEF DESCRIPTION OF THE DRAWINGS
BRIEF DESCRIPTION OF THE DRAWINGS
[0024] FIG. 1 is a perspective view of a honeycomb-type refractory substrate member which may comprise a washcoat composition comprising the catalyst according to an embodiment;
[0025] FIG. 2 is a partial cross-sectional view enlarged relative to FIG.
1 and taken along a plane parallel to the end faces of the substrate of FIG. 1, which shows an enlarged view of one of the gas flow passages shown in FIG. 1;
1 and taken along a plane parallel to the end faces of the substrate of FIG. 1, which shows an enlarged view of one of the gas flow passages shown in FIG. 1;
[0026] FIG. 3 is a graph of crystallite size of the Ce02 as measured by XRD according to the Examples in fresh and after aging at 950 C for 5 hours in 2% 02 and 10%
steam in N2, and
steam in N2, and
[0027] FIG. 4 is a graph of crystallite size of the Ce02 as measured by XRD according to the Examples after aging at 850 C for 8 hours in 10% steam /air.
DETAILED DESCRIPTION
DETAILED DESCRIPTION
[0028] Before describing several exemplary embodiments of the invention, it is to be understood that the invention is not limited to the details of construction or process steps set forth in the following description. The invention is capable of other embodiments and of being practiced or being carried out in various ways.
Date Recue/Date Received 2022-05-20
Date Recue/Date Received 2022-05-20
[0029]
According to embodiments of the invention, it has been discovered that incorporating a barium component (e.g. BaCO3 and/or BaO) into ceria-alumina (Ce02/A1203) has a tremendous stabilization effect on Ce02 and, thus, provides a catalyst material with improved hydrothermal stability, higher NO,, trapping capacity, and higher NO,, conversion 5 than traditional technologies.
According to embodiments of the invention, it has been discovered that incorporating a barium component (e.g. BaCO3 and/or BaO) into ceria-alumina (Ce02/A1203) has a tremendous stabilization effect on Ce02 and, thus, provides a catalyst material with improved hydrothermal stability, higher NO,, trapping capacity, and higher NO,, conversion 5 than traditional technologies.
[0030] In one or more embodiments, a catalyst comprises ceria-alumina particles having a ceria phase present in a weight percent of the composite in the range of about 20% to about 80% on an oxide basis, and an alkaline earth metal component supported on the ceria-alumina particles. The average Ce02 crystallite size of the fresh and aged samples, obtained from XRD, can be used as a measurement for Ce02 hydrothermal stability.
Accordingly, in one or more embodiments, the Ce02 is present in the form of crystallites that are hydrothermally stable and have an average crystallite size of less than 160 A after aging at 950 C for 5 hours in 2% 02 and 10% steam in N2.
Accordingly, in one or more embodiments, the Ce02 is present in the form of crystallites that are hydrothermally stable and have an average crystallite size of less than 160 A after aging at 950 C for 5 hours in 2% 02 and 10% steam in N2.
[0031]
With respect to the terms used in this disclosure, the following definitions are provided.
100321 As used herein, the terms "catalyst" or "catalyst material" or "catalytic material"
refer to a material that promotes a reaction.
[0033] As used herein, the terms "layer" and "layered" refer to a structure that is supported on a surface, e.g. a substrate. In one or more embodiments, the catalyst of the present invention is coated as a washcoat on a substrate or substrate member, to form a layer on a substrate.
[0034] As used herein, the tei _______________________________________ tit "washcoat" has its usual meaning in the art of a thin, adherent coating of a catalytic or other material applied to a carrier substrate material, such as a honeycomb-type carrier member, which is sufficiently porous to permit the passage of the gas stream being treated. As is understood in the art, a washcoat is obtained from a dispersion of particles in slurry, which is applied to a substrate, dried and calcined to provide the porous washcoat.
[0035] As used herein, the term "support" refers to the underlying high surface area material upon which additional chemical compounds or elements are carried. The support particles have pores larger than 20 A and a wide pore distribution. As defined herein, such metal oxide supports exclude molecular sieves, specifically, zeolites. In particular embodiments, high surface area refractory metal oxide supports can be utilized, e.g., alumina support materials, also referred to as "gamma alumina" or "activated alumina,"
which typically exhibit a BET surface area in excess of 60 square meters per gram ("m2/g"), often up to about 200 m2/g or higher. Such activated alumina is usually a mixture of the gamma and delta phases of alumina, but may also contain substantial amounts of eta, kappa, and theta alumina phases. Refractory metal oxides other than activated alumina can be used as a support for at least some of the catalytic components in a given catalyst. For example, bulk ceria, zirconia, alpha alumina, silica, titania, and other materials are known for such use.
[0036] In one or more embodiments, the catalyst comprises ceria-alumina particles. The ceria-alumina particles have a ceria phase present in a weight percent of the catalyst in the range of about 20% to about 80% on an oxide basis, including 20%, 25%, 30%, 35%, 40%, 45%, 50%, 55%, 60%, 65%, 70%, 75%, or 80%. In one or more specific embodiment, the average Ce02 crystallite size of the fresh and aged samples, obtained from XRD, can be used as a measurement for Ce02 hydrothermal stability. Accordingly, in one or more embodiments, the Ce02 is present in the form of crystallites that are hydrothermally stable and have an average crystallite size of less than 160 A, including 160, 155, 150, 140, 130, 120, 110, 10.0, 90, 80, 70, 60, 50, 40, 30, 20, 10, and 5 A, after aging at 950 C for 5 hours in 2% 02 and 10%
steam in N2. In a specific embodiment, the ceria-alumina particles include a ceria phase present in a weight percent of the composite in an amount of about 30% to 80%
by weight on an oxide basis. In a very specific embodiment, the ccria-alumina particles include a ceria phase present in a weight percent of the composite in an amount of about 50%
to 80% by weight on an oxide basis.
[0037] In one or more embodiments, the Ce02 is present in the form of crystallites that are hydrothermally stable and are resistant to growth into larger crystallites upon aging at 950 C. As used herein, the term "resistant to growth" means that the crystallites upon aging grow to a size no larger than an average of 160 A. In a specific embodiment, the Ce02 crystallite size, as determined by XRD, after aging the catalytic article at 950 C for 5 hours in 2% 02 and 10% steam/N2 is less than 160 A. According to one or more embodiments, the Ce02 crystallite size of the powder samples and the coated catalysts are different. In the coated catalysts, other washcoat components may have a stabilization effect on Ce02. Therefore, after the same 950 C aging, the Ce02 crystallite size of the coated catalyst is smaller than that of the powder.
[0038] As used herein, the term "average crystallite size" refers to the mean size as determined by XRD described below.
[0039] As used herein, the term "XRD" refers to x-ray diffraction crystallography, which is a method of determining the atomic and molecular structure of a crystal. In XRD, the crystalline atoms cause a beam of x-rays to diffract into many specific directions. By measuring the angles and intensities of these diffracted beams, a three-dimensional image of the density of electrons within the crystal can be produced. From this electron density, the position of the atoms in the crystal can be determined, as well as their chemical bonds, their disorder, and other information. In particular, XRD can be used to estimate crystallite size; the peak width is inversely proportional to crystallite size; as the crystallite size gets smaller, the peak gets broader. In one or more embodiments, XRD is used to measure the average crystallite size of the Ce02 particles.
[0040] The width of an XRD peak is interpreted as a combination of broadening effects related to both size and strain. The formulas used to determine both are given below. The first equation below is the Scherrer equation which is used to transform full width at half maximum intensity, FWHM, information into a crystallite size for a given phase. The second equation is used to calculate strain in a crystal from peak width information and the total width or breadth of a peak considered to be a sum of these two effects as shown in the third equation. It should be noticed that size and strain broadening vary in different fashions with regard to the Bragg angle 0. The constants for the Scherrer equation are discussed below.
KA
13L = ____________________________________ L cos9 Pe = CE tane KA.
13tot = 13e + 13L = CE tan0 + ____________________ L cos0 [0041] The constants for the Scherrer equation are [0042] K: shape constant, we use a value of 0.9 [0043] L: the peak width, this is corrected for the contribution from the instrumental optics through the use of NEST SRM 660b LaB6 Line Position & Line Shape Standard [0044] 0: 1/2 of the 20 value of the reflection of interest [0045] X: wavelength of radiation 1.5406A
[0046] As used herein, "crystallite size" is understood to be the length of the coherent scattering domain in a direction orthogonal to the set of lattice planes which give rise to the reflection. For Ce02, the CeO2 <111> reflection is the most intense peak in the X-ray diffraction pattem of Ce02. The Ce02 <111> plane of atoms intersects each of the crystallographic axes at unity and is orthogonal to the body diagonal represented by the <111>
vector. So, a crystallite size of 312A calculated from the FWHM of the Ce02 111 reflection would be considered to be roughly 100 layers of the <111> plane of atoms.
[0047] Different directions, and thus reflections, in a crystal will generate different though close crystallite size values. The values will be exact only if the crystal is a perfect sphere. A
Williamson Hall plot is used to interpret size and strain effects by considering the total peak breadth as a linear equation below with the slope of the line representing strain and the intercept being the size of a crystal.
KX
Not cost) = Cg sin0 +
[0048] To determine the crystallite size of a material FWHM value of a single reflection or from the complete X-ray diffraction pattern is determined. Traditionally a single reflection has been fit to determine the FWHM value of that reflection, corrected the FWHM
value for the contribution from the instrument, and then converted the corrected FWHM value into a crystallite size value using the Scherrer equation. This would be done by ignoring any effect from strain in the crystal. This method has been used primarily for questions concerning the crystallite size of precious metals for which we have only a single useful reflection. It should be noted that in fitting peaks it is desired to have a clean reflection which is not overlapped by reflections from other phases. This is rarely the case with present washcoat formulations Rietveld methods are now used. Rietveld methods allow the fit of complex X-ray diffraction patterns using the known crystal structures of the phases present. The crystal structures act as restraints or brakes on the fitting process. Phase content, lattice parameters, and FWHM
info' __ illation are varied for each phase until the overall model matches the experimental data.
[0049] In the Examples below, Rietveld methods were used to fit experimental patterns for fresh and aged samples. A FWHM curve determined for each phase in each sample was used to determine a crystallite size. Strain effects were excluded.
[0050] As used herein, the term "alkaline earth metal" refers to one or more chemical elements 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, the alkaline earth metal component can be incorporated into the catalyst as a salt and/or sulfate and/or oxide (e.g., BaCO3, BaSO4, and/or BaO) to provide an "alkaline earth metal component". It is noted that upon calcination, the barium component will convert to barium carbonate and/or barium oxide. In one or more embodiments, the alkaline earth metal component comprises a barium component. The alkaline earth metal component can be present in the washcoat in an amount in the range of about 0.5% to 50% by weight on an oxide basis, including 0.5, 1, 2, 3, 4, 5, 10, 15, 20, 25, 30, 35, 40, 45, and 50%.
In a specific embodiment, the alkaline earth metal component comprises a barium component, which is present in an amount in the range of about 0.5% to about 50% by weight on an oxide basis. In other specific embodiments, the alkaline earth metal component comprises a barium component, which is present in an amount in the range of about 5% to about 30%
by weight on an oxide basis.
[0051] In one or more embodiments, the Ce02 crystallite size of the aged .samples, obtained from XRD, was used as a measurement for alkaline carth/Ce/Al hydrothermal stability.
[0052] In specific embodiments, a tremendous stabilization effect is observed when the ceria-alumina particles are impregnated with barium precursors, particularly water-soluble barium precursor salts (e.g. barium acetate), which are calcined to provide barium carbonate (BaCO3) and/or barium oxide (Ba0). Referring to FIG. 3, after aging at 950 C
for 5 hours in 2% 02 and 10% steam in N2, the Ce02 crystallite sizes of the BaCO3/(Ce02-A1203) samples were within about 75 to about 160 A. This is remarkably lower than that of aged BaCO3/Ce02 powder (>1000 A). Alternative BaCO3 loadings were applied on 70% Ce02/A1203 powder to determine if they can also provide a similar effect. Referring to FIG. 4, after aging at 850 C
for 8 hr in 10% steam/air, the samples loaded with 15, 10, and 5 wt% barium component (calculated as barium oxide) show much lower Ce02 crystallite size than the BaCO3/Ce02.
Overall, it appears that the barium component (e.g. BaCO3 and/or BaO) has a unique stabilization effect on ceria crystallite growth in a Ba/Ce/A1 system. This stabilization effect is likely beneficial, for example, for NO, trapping in LNT catalysts. The additional ceria surface area resulting from smaller crystallite sizes will allow for more low temperature ceria based NO, trapping, improve WGS, and improve PGM dispersion.
5 [0053] Thus, according to one or morc embodiments, the ceria is destabilized in a Ba-Ce system, and is significantly stabilized in a Ba-Cc-Al system.
[0054] In one or more embodiments, without intending to be bound by theory, it is thought that the additional ceria surface area resulting from smaller crystallite sizes allows for higher BaCO3 based NO trapping due to better BaCO3 dispersing, higher Ce02 based NO
trapping at 10 low temperature, improved NO, reduction due to more efficient WGS, and improved NO
oxidation and NO, reduction due to better PGM dispersion. Thus, incorporating barium (BaCO3 and/or BaO) into ceria-alumina (Ce02/A1203) has a tremendous stabilization effect on Ce02 and provides a catalyst material with improved hydrothermal stability, higher NOx trapping capacity, and higher NO, conversion than traditional technologies.
[0055] In one or more embodiments, the catalyst of the present invention exhibits improved NO, trapping capacity during lean operation and improved NO, reduction during rich regeneration, after aging at 950 C for 5 hours in 2% 02 and 10%
steam/N2. The improvement is over traditional catalysts that comprise ceria not incorporated with Al2O3.
[0056] In one or more embodiments, the catalyst of the invention can be utilized as a three-way catalyst (TWC), a diesel oxidation catalyst (DOC), a gasoline particulate filter (GPF), a lean NO, trap (LNT), an integrated LNT-TWC, or as an ammonia oxidation catalyst (AM0x).
[0057] In one or more embodiments, the catalyst further comprises at least one platinum group metal supported on the barium(ceria-alumina) particles. As used herein, the teun "platinum group metal" or "PGM" refers to one or more chemical elements defined in the Periodic Table of Elements, including platinum, palladium, rhodium, osmium, iridium, and ruthenium, and mixtures thereof. In one or more embodiments, the platinum group metal is selected from the group consisting of platinum, palladium, rhodium, iridium, and mixtures thereof In a specific embodiment, the platinum group metal is selected from platinum, palladium, rhodium, and mixtures thereof. Generally, there are no specific restrictions as far as the total platinum group metal content of the catalyst is concerned.
[0058] Typically, the catalyst of the present invention is disposed on a substrate. The substrate may be any of those materials typically used for preparing catalysts, and will typically comprise a ceramic or metal honeycomb structure. Any suitable substrate may be employed, such as a monolithic substrate of the type having fine, parallel gas flow passages extending therethrough from an inlet or an outlet face of the substrate, such that passages are open to fluid flow therethrough (referred to herein as flow-through substrates). The passages, which arc essentially straight paths from their fluid inlet to their fluid outlet, arc defined by walls on which the catalytic material is coated as a washcoat so that the gases flowing through the passages contact the catalytic material. The flow passages of the monolithic substrate are thin-walled channels, which can be of any suitable cross-sectional shape and size such as trapezoidal, rectangular, square, sinusoidal, hexagonal, oval, circular, etc.
[0059] Such monolithic substrates may contain up to about 900 or more flow passages (or "cells") per square inch of cross section, although far fewer may be used. For example, the substrate may have from about 7 to 600, more usually from about 100 to 400, cells per square inch ("cpsi"). The cells can have cross sections that are rectangular, square, circular, oval, triangular, hexagonal, or are of other polygonal shapes. The ceramic substrate may be made of any suitable refractory material, e.g., cordierite, cordierite-alumina, silicon nitride, or silicon carbide, or the substrates may be composed of one or more metals or metal alloys.
[0060] The catalyst according to embodiments of the present invention can be applied to the substrate surfaces by any known means in the art. For example, the catalyst washcoat can be applied by spray coating, powder coating, or brushing or dipping a surface into the catalyst composition.
[0061] In one or more embodiments, the catalyst is disposed on a honeycomb substrate.
[0062] When applied as a washcoat, the invention may be more readily appreciated by reference to FIGS. 1 and 2. FIGS. 1 and 2 show a refractory substrate member 2, in accordance with one embodiment of the present invention. Referring to FIG. 1, the refractory substrate member 2 is a cylindrical shape having a cylindrical outer surface 4, an upstream end face 6 and a downstream end face 8, which is identical to end face 6.
Substrate member 2 has a plurality of fine, parallel gas flow passages 10 formed therein. As seen in FIG. 2 flow passages 10 are formed by walls 12 and extend through substrate from upstream end face 6 to downstream end face 8, the passages 10 being unobstructed so as to permit the flow of a fluid, e.g., a gas stream, longitudinally through substrate via gas flow passages 10 thereof. A
discrete catalyst layer 14, which in the art and sometimes below is referred to as a "washcoat", is adhered or coated onto the walls 12 of the substrate member. In some embodiments, an additional catalyst layer 16 is coated on top of the catalyst layer 14. The second catalyst layer 16 can be the same composition as the catalyst layer 14, or the second catalyst layer 16 can comprise a distinct catalyst composition.
[0063] As shown in FIG. 2, the substrate member includes void spaces provided by the gas-flow passages 10, and the cross-sectional area of these passages 10 and the thickness of the walls 12 defining the passages will vary from one type of substrate member to another.
Similarly, the weight of washcoat applied to such substrates will vary from case to case.
Consequently, in describing the quantity of washcoat or catalytic metal component or other component of the composition, it is convenient to use units of weight of component per unit volume of substrate. Therefore, the units of grams per cubic inch ("g/in") and grams per cubic foot ("gift") are used herein to mean the weight of a component per volume of the substrate member, including the volume of void spaces of the substrate member.
[0064] In a second aspect of the invention, the catalyst of one or more embodiments can be used in an integrated emission treatment system comprising one or more additional components for the treatment of exhaust gas emissions. For example, the emission treatment system may comprise a lean bum engine upstream from the catalyst of one or more embodiments, and may further comprise a second catalyst and, optionally, a particulate filter.
In one or more embodiments, the second catalyst is selected from a three-way catalyst (TWC), gasoline particulate filter (GPF), selective catalytic reduction (SCR), lean NO trap (LNT), ammonia oxidation (AM0x), SCR on a filter (SCRoF), and combinations thereof, and combinations thereof. In one or more embodiments, the particulate filter can be selected from a gasoline particulate filter, a soot filter, or a SCRoF. The particulate filter may be catalyzed for specific functions. The catalyst can be located upstream or downstream of the particulate filter.
[0065] In one or more embodiments, the emission treatment system may comprise a lean bum engine upstream from the catalyst of one or more embodiments, and may further comprise a TWC. In one or more embodiments, the emission treatment system can further comprise an SCR/LNT.
[0066] In a specific embodiment, the particulate filter is a catalyzed soot filter (CSF). The CSF can comprise a substrate coated with a washcoat layer containing one or more catalysts for burning off trapped soot and or oxidizing exhaust gas stream emissions. In general, the soot burning catalyst can be any known catalyst for combustion of soot. For example, the CSF
can be coated with a one or more high surface area refractory oxides (e.g., alumina, silica, silica alumina, zirconia, and zirconia alumina) and/or an oxidation catalyst (e.g., a ceria-zirconia) for the combustion of unburned hydrocarbons and to some degree particulate matter.
In one or more embodiments, the soot burning catalyst is an oxidation catalyst comprising one or more precious metal (PM) catalysts (platinum, palladium, and/or rhodium).
100671 In general, any known filter substrate in the art can be used, including, e.g., a honeycomb wall flow filter, wound or packed fiber filter, open-cell foam, sintered metal filter, etc., with wall flow filters being specifically exemplified. Wall flow substrates useful for supporting the CSF compositions have a plurality of fine, substantially parallel gas flow passages extending along the longitudinal axis of the substrate. Typically, each passage is blocked at one end of the substrate body, with alternate passages blocked at opposite end-faces.
Such monolithic substrates may contain up to about 900 or more flow passages (or "cells") per square inch of cross section, although far fewer may be used. For example, the substrate may have from about 7 to 600, more usually from about 100 to 400, cells per square inch ("cpsi").
The porous wall flow filter used in embodiments of the invention is optionally catalyzed in that the wall of said element has thereon or contained therein one or more catalytic materials, such CSF catalyst compositions are described hereinabove. Catalytic materials may be present on the inlet side of the element wall alone, the outlet side alone, both the inlet and outlet sides, or the wall itself may consist all, or in part, of the catalytic material. In another embodiment, this invention may include the use of one or more washcoat layers of catalytic materials and combinations of one or more washcoat layers of catalytic materials on the inlet and/or outlet walls of the element.
100681 The invention is now described with reference to the following examples. Before describing several exemplary embodiments of the invention, it is to be understood that the invention is not limited to the details of construction or process steps set forth in the following description. The invention is capable of other embodiments and of being practiced or being carried out in various ways.
EXAMPLES
.. EXAMPLE 1¨ PREPARATION OF CATALYST
[0069] Ce02-A1203 particles (1A through 5A) were impregnated with a barium acetate solution to provide samples 1B through 5B having BaCO3/(Ce02-A1203) with a BaCO3 content as specified in Table 1. The mixture was dried at 110 C and calcined at 720 C for 2 hours.
[0070] Ce02-A1203 particles (4A) were impregnated with a barium acetate solution to provide 4C through 4E having BaCO3/(Ce02-A1203) with a BaCO3 content as specified in Table 1. The mixture was dried at 110 C and calcined at 620 C for 2 hours.
[0071] Ce02 particles (6A) were impregnated with a barium acetate solution to provide 6B
and 6C having BaCO3/Ce02 with a BaCO3 content as specified in Table 1. The mixture was dried at 110 C and calcined at 600 C for 2 hours.
[0072] Referring to FIG. 3, after aging at 950 C for 5 hours in 2% 02 and 10% steam in N2, the Ce02 crystallite sizes of the BaCO3/(Ce02-A1203) samples 1B-5B were within 79 to 158 A.
100731 Referring to FIG. 4, the Ce02 crystallite sizes of the BaCO3/(Ce02-A1203) samples 4C through 4E were within 73 to 92 A after aging at 850 C for 8 hours in 10%
steam in air.
[0074] Table 1 shows the content of IA through 6A, and 1B through 6B, 6C, 4C through 4E.
100751 Table 1 Sample BaCO3 Ce02 A1203 BET Surface Area, m2/g wt% wt% wt% As is 950 C aged*
lA 0 30 70 *Aging conditions: 950 C for 5 hours in 2% 02 and 10% steam in N2 EXAMPLE 2¨ XRD MEASUREMENT
[0076] The Ce02 crystallite size of the Example 1 samples was measured by XRD. The 5 samples were ground using a mortar and pestle. The resultant powders were then back packed into flat plate mounts for analysis. A 0-0 PANalytical X'Pert Pro MPD X-ray diffraction system was used to collect data in Bragg-Brentano geometry. The optical path consisted of the X-ray tube, 0.04 rad soller slit, 1/4 divergence slit, 15mm beam mask, 1/2 anti-scatter slit, the sample, 1/4 anti-scatter slit, 0.04 rad soller slit, Ni filter, and a P1Xcel linear position 10 sensitive detector with a 2.114 active length. Cuka radiation was used in the analysis with generator settings of 45kV and 40mA. X-ray diffraction data was collected from 100 to 90 20 using a step size of 0.026 and a count time of 600s per step. Phase identification was done using Jade software. All numerical values were determined using Rietveld methods.
[0077] Reference throughout this specification to "one embodiment,"
"certain 15 embodiments," "one or more embodiments" or "an embodiment" means that a particular feature, structure, material, or characteristic described in connection with the embodiment is included in at least one embodiment of the invention. Thus, the appearances of the phrases such as "in one or more embodiments," "in certain embodiments," "in one embodiment" or "in an embodiment" in various places throughout this specification are not necessarily referring to the same embodiment of the invention. Furthermore, the particular features, structures, materials, or characteristics may be combined in any suitable manner in one or more embodiments. The order of description of the above method should not be considered limiting, and methods may use the described operations out of order or with omissions or additions.
[0078] It is to be understood that the above description is intended to be illustrative, and not restrictive. Many other embodiments will be apparent to those of ordinary skill in the art upon reviewing the above description. The scope of the invention should, therefore, be determined with reference to the appended claims, along with the full scope of equivalents to which such claims are entitled.
With respect to the terms used in this disclosure, the following definitions are provided.
100321 As used herein, the terms "catalyst" or "catalyst material" or "catalytic material"
refer to a material that promotes a reaction.
[0033] As used herein, the terms "layer" and "layered" refer to a structure that is supported on a surface, e.g. a substrate. In one or more embodiments, the catalyst of the present invention is coated as a washcoat on a substrate or substrate member, to form a layer on a substrate.
[0034] As used herein, the tei _______________________________________ tit "washcoat" has its usual meaning in the art of a thin, adherent coating of a catalytic or other material applied to a carrier substrate material, such as a honeycomb-type carrier member, which is sufficiently porous to permit the passage of the gas stream being treated. As is understood in the art, a washcoat is obtained from a dispersion of particles in slurry, which is applied to a substrate, dried and calcined to provide the porous washcoat.
[0035] As used herein, the term "support" refers to the underlying high surface area material upon which additional chemical compounds or elements are carried. The support particles have pores larger than 20 A and a wide pore distribution. As defined herein, such metal oxide supports exclude molecular sieves, specifically, zeolites. In particular embodiments, high surface area refractory metal oxide supports can be utilized, e.g., alumina support materials, also referred to as "gamma alumina" or "activated alumina,"
which typically exhibit a BET surface area in excess of 60 square meters per gram ("m2/g"), often up to about 200 m2/g or higher. Such activated alumina is usually a mixture of the gamma and delta phases of alumina, but may also contain substantial amounts of eta, kappa, and theta alumina phases. Refractory metal oxides other than activated alumina can be used as a support for at least some of the catalytic components in a given catalyst. For example, bulk ceria, zirconia, alpha alumina, silica, titania, and other materials are known for such use.
[0036] In one or more embodiments, the catalyst comprises ceria-alumina particles. The ceria-alumina particles have a ceria phase present in a weight percent of the catalyst in the range of about 20% to about 80% on an oxide basis, including 20%, 25%, 30%, 35%, 40%, 45%, 50%, 55%, 60%, 65%, 70%, 75%, or 80%. In one or more specific embodiment, the average Ce02 crystallite size of the fresh and aged samples, obtained from XRD, can be used as a measurement for Ce02 hydrothermal stability. Accordingly, in one or more embodiments, the Ce02 is present in the form of crystallites that are hydrothermally stable and have an average crystallite size of less than 160 A, including 160, 155, 150, 140, 130, 120, 110, 10.0, 90, 80, 70, 60, 50, 40, 30, 20, 10, and 5 A, after aging at 950 C for 5 hours in 2% 02 and 10%
steam in N2. In a specific embodiment, the ceria-alumina particles include a ceria phase present in a weight percent of the composite in an amount of about 30% to 80%
by weight on an oxide basis. In a very specific embodiment, the ccria-alumina particles include a ceria phase present in a weight percent of the composite in an amount of about 50%
to 80% by weight on an oxide basis.
[0037] In one or more embodiments, the Ce02 is present in the form of crystallites that are hydrothermally stable and are resistant to growth into larger crystallites upon aging at 950 C. As used herein, the term "resistant to growth" means that the crystallites upon aging grow to a size no larger than an average of 160 A. In a specific embodiment, the Ce02 crystallite size, as determined by XRD, after aging the catalytic article at 950 C for 5 hours in 2% 02 and 10% steam/N2 is less than 160 A. According to one or more embodiments, the Ce02 crystallite size of the powder samples and the coated catalysts are different. In the coated catalysts, other washcoat components may have a stabilization effect on Ce02. Therefore, after the same 950 C aging, the Ce02 crystallite size of the coated catalyst is smaller than that of the powder.
[0038] As used herein, the term "average crystallite size" refers to the mean size as determined by XRD described below.
[0039] As used herein, the term "XRD" refers to x-ray diffraction crystallography, which is a method of determining the atomic and molecular structure of a crystal. In XRD, the crystalline atoms cause a beam of x-rays to diffract into many specific directions. By measuring the angles and intensities of these diffracted beams, a three-dimensional image of the density of electrons within the crystal can be produced. From this electron density, the position of the atoms in the crystal can be determined, as well as their chemical bonds, their disorder, and other information. In particular, XRD can be used to estimate crystallite size; the peak width is inversely proportional to crystallite size; as the crystallite size gets smaller, the peak gets broader. In one or more embodiments, XRD is used to measure the average crystallite size of the Ce02 particles.
[0040] The width of an XRD peak is interpreted as a combination of broadening effects related to both size and strain. The formulas used to determine both are given below. The first equation below is the Scherrer equation which is used to transform full width at half maximum intensity, FWHM, information into a crystallite size for a given phase. The second equation is used to calculate strain in a crystal from peak width information and the total width or breadth of a peak considered to be a sum of these two effects as shown in the third equation. It should be noticed that size and strain broadening vary in different fashions with regard to the Bragg angle 0. The constants for the Scherrer equation are discussed below.
KA
13L = ____________________________________ L cos9 Pe = CE tane KA.
13tot = 13e + 13L = CE tan0 + ____________________ L cos0 [0041] The constants for the Scherrer equation are [0042] K: shape constant, we use a value of 0.9 [0043] L: the peak width, this is corrected for the contribution from the instrumental optics through the use of NEST SRM 660b LaB6 Line Position & Line Shape Standard [0044] 0: 1/2 of the 20 value of the reflection of interest [0045] X: wavelength of radiation 1.5406A
[0046] As used herein, "crystallite size" is understood to be the length of the coherent scattering domain in a direction orthogonal to the set of lattice planes which give rise to the reflection. For Ce02, the CeO2 <111> reflection is the most intense peak in the X-ray diffraction pattem of Ce02. The Ce02 <111> plane of atoms intersects each of the crystallographic axes at unity and is orthogonal to the body diagonal represented by the <111>
vector. So, a crystallite size of 312A calculated from the FWHM of the Ce02 111 reflection would be considered to be roughly 100 layers of the <111> plane of atoms.
[0047] Different directions, and thus reflections, in a crystal will generate different though close crystallite size values. The values will be exact only if the crystal is a perfect sphere. A
Williamson Hall plot is used to interpret size and strain effects by considering the total peak breadth as a linear equation below with the slope of the line representing strain and the intercept being the size of a crystal.
KX
Not cost) = Cg sin0 +
[0048] To determine the crystallite size of a material FWHM value of a single reflection or from the complete X-ray diffraction pattern is determined. Traditionally a single reflection has been fit to determine the FWHM value of that reflection, corrected the FWHM
value for the contribution from the instrument, and then converted the corrected FWHM value into a crystallite size value using the Scherrer equation. This would be done by ignoring any effect from strain in the crystal. This method has been used primarily for questions concerning the crystallite size of precious metals for which we have only a single useful reflection. It should be noted that in fitting peaks it is desired to have a clean reflection which is not overlapped by reflections from other phases. This is rarely the case with present washcoat formulations Rietveld methods are now used. Rietveld methods allow the fit of complex X-ray diffraction patterns using the known crystal structures of the phases present. The crystal structures act as restraints or brakes on the fitting process. Phase content, lattice parameters, and FWHM
info' __ illation are varied for each phase until the overall model matches the experimental data.
[0049] In the Examples below, Rietveld methods were used to fit experimental patterns for fresh and aged samples. A FWHM curve determined for each phase in each sample was used to determine a crystallite size. Strain effects were excluded.
[0050] As used herein, the term "alkaline earth metal" refers to one or more chemical elements 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, the alkaline earth metal component can be incorporated into the catalyst as a salt and/or sulfate and/or oxide (e.g., BaCO3, BaSO4, and/or BaO) to provide an "alkaline earth metal component". It is noted that upon calcination, the barium component will convert to barium carbonate and/or barium oxide. In one or more embodiments, the alkaline earth metal component comprises a barium component. The alkaline earth metal component can be present in the washcoat in an amount in the range of about 0.5% to 50% by weight on an oxide basis, including 0.5, 1, 2, 3, 4, 5, 10, 15, 20, 25, 30, 35, 40, 45, and 50%.
In a specific embodiment, the alkaline earth metal component comprises a barium component, which is present in an amount in the range of about 0.5% to about 50% by weight on an oxide basis. In other specific embodiments, the alkaline earth metal component comprises a barium component, which is present in an amount in the range of about 5% to about 30%
by weight on an oxide basis.
[0051] In one or more embodiments, the Ce02 crystallite size of the aged .samples, obtained from XRD, was used as a measurement for alkaline carth/Ce/Al hydrothermal stability.
[0052] In specific embodiments, a tremendous stabilization effect is observed when the ceria-alumina particles are impregnated with barium precursors, particularly water-soluble barium precursor salts (e.g. barium acetate), which are calcined to provide barium carbonate (BaCO3) and/or barium oxide (Ba0). Referring to FIG. 3, after aging at 950 C
for 5 hours in 2% 02 and 10% steam in N2, the Ce02 crystallite sizes of the BaCO3/(Ce02-A1203) samples were within about 75 to about 160 A. This is remarkably lower than that of aged BaCO3/Ce02 powder (>1000 A). Alternative BaCO3 loadings were applied on 70% Ce02/A1203 powder to determine if they can also provide a similar effect. Referring to FIG. 4, after aging at 850 C
for 8 hr in 10% steam/air, the samples loaded with 15, 10, and 5 wt% barium component (calculated as barium oxide) show much lower Ce02 crystallite size than the BaCO3/Ce02.
Overall, it appears that the barium component (e.g. BaCO3 and/or BaO) has a unique stabilization effect on ceria crystallite growth in a Ba/Ce/A1 system. This stabilization effect is likely beneficial, for example, for NO, trapping in LNT catalysts. The additional ceria surface area resulting from smaller crystallite sizes will allow for more low temperature ceria based NO, trapping, improve WGS, and improve PGM dispersion.
5 [0053] Thus, according to one or morc embodiments, the ceria is destabilized in a Ba-Ce system, and is significantly stabilized in a Ba-Cc-Al system.
[0054] In one or more embodiments, without intending to be bound by theory, it is thought that the additional ceria surface area resulting from smaller crystallite sizes allows for higher BaCO3 based NO trapping due to better BaCO3 dispersing, higher Ce02 based NO
trapping at 10 low temperature, improved NO, reduction due to more efficient WGS, and improved NO
oxidation and NO, reduction due to better PGM dispersion. Thus, incorporating barium (BaCO3 and/or BaO) into ceria-alumina (Ce02/A1203) has a tremendous stabilization effect on Ce02 and provides a catalyst material with improved hydrothermal stability, higher NOx trapping capacity, and higher NO, conversion than traditional technologies.
[0055] In one or more embodiments, the catalyst of the present invention exhibits improved NO, trapping capacity during lean operation and improved NO, reduction during rich regeneration, after aging at 950 C for 5 hours in 2% 02 and 10%
steam/N2. The improvement is over traditional catalysts that comprise ceria not incorporated with Al2O3.
[0056] In one or more embodiments, the catalyst of the invention can be utilized as a three-way catalyst (TWC), a diesel oxidation catalyst (DOC), a gasoline particulate filter (GPF), a lean NO, trap (LNT), an integrated LNT-TWC, or as an ammonia oxidation catalyst (AM0x).
[0057] In one or more embodiments, the catalyst further comprises at least one platinum group metal supported on the barium(ceria-alumina) particles. As used herein, the teun "platinum group metal" or "PGM" refers to one or more chemical elements defined in the Periodic Table of Elements, including platinum, palladium, rhodium, osmium, iridium, and ruthenium, and mixtures thereof. In one or more embodiments, the platinum group metal is selected from the group consisting of platinum, palladium, rhodium, iridium, and mixtures thereof In a specific embodiment, the platinum group metal is selected from platinum, palladium, rhodium, and mixtures thereof. Generally, there are no specific restrictions as far as the total platinum group metal content of the catalyst is concerned.
[0058] Typically, the catalyst of the present invention is disposed on a substrate. The substrate may be any of those materials typically used for preparing catalysts, and will typically comprise a ceramic or metal honeycomb structure. Any suitable substrate may be employed, such as a monolithic substrate of the type having fine, parallel gas flow passages extending therethrough from an inlet or an outlet face of the substrate, such that passages are open to fluid flow therethrough (referred to herein as flow-through substrates). The passages, which arc essentially straight paths from their fluid inlet to their fluid outlet, arc defined by walls on which the catalytic material is coated as a washcoat so that the gases flowing through the passages contact the catalytic material. The flow passages of the monolithic substrate are thin-walled channels, which can be of any suitable cross-sectional shape and size such as trapezoidal, rectangular, square, sinusoidal, hexagonal, oval, circular, etc.
[0059] Such monolithic substrates may contain up to about 900 or more flow passages (or "cells") per square inch of cross section, although far fewer may be used. For example, the substrate may have from about 7 to 600, more usually from about 100 to 400, cells per square inch ("cpsi"). The cells can have cross sections that are rectangular, square, circular, oval, triangular, hexagonal, or are of other polygonal shapes. The ceramic substrate may be made of any suitable refractory material, e.g., cordierite, cordierite-alumina, silicon nitride, or silicon carbide, or the substrates may be composed of one or more metals or metal alloys.
[0060] The catalyst according to embodiments of the present invention can be applied to the substrate surfaces by any known means in the art. For example, the catalyst washcoat can be applied by spray coating, powder coating, or brushing or dipping a surface into the catalyst composition.
[0061] In one or more embodiments, the catalyst is disposed on a honeycomb substrate.
[0062] When applied as a washcoat, the invention may be more readily appreciated by reference to FIGS. 1 and 2. FIGS. 1 and 2 show a refractory substrate member 2, in accordance with one embodiment of the present invention. Referring to FIG. 1, the refractory substrate member 2 is a cylindrical shape having a cylindrical outer surface 4, an upstream end face 6 and a downstream end face 8, which is identical to end face 6.
Substrate member 2 has a plurality of fine, parallel gas flow passages 10 formed therein. As seen in FIG. 2 flow passages 10 are formed by walls 12 and extend through substrate from upstream end face 6 to downstream end face 8, the passages 10 being unobstructed so as to permit the flow of a fluid, e.g., a gas stream, longitudinally through substrate via gas flow passages 10 thereof. A
discrete catalyst layer 14, which in the art and sometimes below is referred to as a "washcoat", is adhered or coated onto the walls 12 of the substrate member. In some embodiments, an additional catalyst layer 16 is coated on top of the catalyst layer 14. The second catalyst layer 16 can be the same composition as the catalyst layer 14, or the second catalyst layer 16 can comprise a distinct catalyst composition.
[0063] As shown in FIG. 2, the substrate member includes void spaces provided by the gas-flow passages 10, and the cross-sectional area of these passages 10 and the thickness of the walls 12 defining the passages will vary from one type of substrate member to another.
Similarly, the weight of washcoat applied to such substrates will vary from case to case.
Consequently, in describing the quantity of washcoat or catalytic metal component or other component of the composition, it is convenient to use units of weight of component per unit volume of substrate. Therefore, the units of grams per cubic inch ("g/in") and grams per cubic foot ("gift") are used herein to mean the weight of a component per volume of the substrate member, including the volume of void spaces of the substrate member.
[0064] In a second aspect of the invention, the catalyst of one or more embodiments can be used in an integrated emission treatment system comprising one or more additional components for the treatment of exhaust gas emissions. For example, the emission treatment system may comprise a lean bum engine upstream from the catalyst of one or more embodiments, and may further comprise a second catalyst and, optionally, a particulate filter.
In one or more embodiments, the second catalyst is selected from a three-way catalyst (TWC), gasoline particulate filter (GPF), selective catalytic reduction (SCR), lean NO trap (LNT), ammonia oxidation (AM0x), SCR on a filter (SCRoF), and combinations thereof, and combinations thereof. In one or more embodiments, the particulate filter can be selected from a gasoline particulate filter, a soot filter, or a SCRoF. The particulate filter may be catalyzed for specific functions. The catalyst can be located upstream or downstream of the particulate filter.
[0065] In one or more embodiments, the emission treatment system may comprise a lean bum engine upstream from the catalyst of one or more embodiments, and may further comprise a TWC. In one or more embodiments, the emission treatment system can further comprise an SCR/LNT.
[0066] In a specific embodiment, the particulate filter is a catalyzed soot filter (CSF). The CSF can comprise a substrate coated with a washcoat layer containing one or more catalysts for burning off trapped soot and or oxidizing exhaust gas stream emissions. In general, the soot burning catalyst can be any known catalyst for combustion of soot. For example, the CSF
can be coated with a one or more high surface area refractory oxides (e.g., alumina, silica, silica alumina, zirconia, and zirconia alumina) and/or an oxidation catalyst (e.g., a ceria-zirconia) for the combustion of unburned hydrocarbons and to some degree particulate matter.
In one or more embodiments, the soot burning catalyst is an oxidation catalyst comprising one or more precious metal (PM) catalysts (platinum, palladium, and/or rhodium).
100671 In general, any known filter substrate in the art can be used, including, e.g., a honeycomb wall flow filter, wound or packed fiber filter, open-cell foam, sintered metal filter, etc., with wall flow filters being specifically exemplified. Wall flow substrates useful for supporting the CSF compositions have a plurality of fine, substantially parallel gas flow passages extending along the longitudinal axis of the substrate. Typically, each passage is blocked at one end of the substrate body, with alternate passages blocked at opposite end-faces.
Such monolithic substrates may contain up to about 900 or more flow passages (or "cells") per square inch of cross section, although far fewer may be used. For example, the substrate may have from about 7 to 600, more usually from about 100 to 400, cells per square inch ("cpsi").
The porous wall flow filter used in embodiments of the invention is optionally catalyzed in that the wall of said element has thereon or contained therein one or more catalytic materials, such CSF catalyst compositions are described hereinabove. Catalytic materials may be present on the inlet side of the element wall alone, the outlet side alone, both the inlet and outlet sides, or the wall itself may consist all, or in part, of the catalytic material. In another embodiment, this invention may include the use of one or more washcoat layers of catalytic materials and combinations of one or more washcoat layers of catalytic materials on the inlet and/or outlet walls of the element.
100681 The invention is now described with reference to the following examples. Before describing several exemplary embodiments of the invention, it is to be understood that the invention is not limited to the details of construction or process steps set forth in the following description. The invention is capable of other embodiments and of being practiced or being carried out in various ways.
EXAMPLES
.. EXAMPLE 1¨ PREPARATION OF CATALYST
[0069] Ce02-A1203 particles (1A through 5A) were impregnated with a barium acetate solution to provide samples 1B through 5B having BaCO3/(Ce02-A1203) with a BaCO3 content as specified in Table 1. The mixture was dried at 110 C and calcined at 720 C for 2 hours.
[0070] Ce02-A1203 particles (4A) were impregnated with a barium acetate solution to provide 4C through 4E having BaCO3/(Ce02-A1203) with a BaCO3 content as specified in Table 1. The mixture was dried at 110 C and calcined at 620 C for 2 hours.
[0071] Ce02 particles (6A) were impregnated with a barium acetate solution to provide 6B
and 6C having BaCO3/Ce02 with a BaCO3 content as specified in Table 1. The mixture was dried at 110 C and calcined at 600 C for 2 hours.
[0072] Referring to FIG. 3, after aging at 950 C for 5 hours in 2% 02 and 10% steam in N2, the Ce02 crystallite sizes of the BaCO3/(Ce02-A1203) samples 1B-5B were within 79 to 158 A.
100731 Referring to FIG. 4, the Ce02 crystallite sizes of the BaCO3/(Ce02-A1203) samples 4C through 4E were within 73 to 92 A after aging at 850 C for 8 hours in 10%
steam in air.
[0074] Table 1 shows the content of IA through 6A, and 1B through 6B, 6C, 4C through 4E.
100751 Table 1 Sample BaCO3 Ce02 A1203 BET Surface Area, m2/g wt% wt% wt% As is 950 C aged*
lA 0 30 70 *Aging conditions: 950 C for 5 hours in 2% 02 and 10% steam in N2 EXAMPLE 2¨ XRD MEASUREMENT
[0076] The Ce02 crystallite size of the Example 1 samples was measured by XRD. The 5 samples were ground using a mortar and pestle. The resultant powders were then back packed into flat plate mounts for analysis. A 0-0 PANalytical X'Pert Pro MPD X-ray diffraction system was used to collect data in Bragg-Brentano geometry. The optical path consisted of the X-ray tube, 0.04 rad soller slit, 1/4 divergence slit, 15mm beam mask, 1/2 anti-scatter slit, the sample, 1/4 anti-scatter slit, 0.04 rad soller slit, Ni filter, and a P1Xcel linear position 10 sensitive detector with a 2.114 active length. Cuka radiation was used in the analysis with generator settings of 45kV and 40mA. X-ray diffraction data was collected from 100 to 90 20 using a step size of 0.026 and a count time of 600s per step. Phase identification was done using Jade software. All numerical values were determined using Rietveld methods.
[0077] Reference throughout this specification to "one embodiment,"
"certain 15 embodiments," "one or more embodiments" or "an embodiment" means that a particular feature, structure, material, or characteristic described in connection with the embodiment is included in at least one embodiment of the invention. Thus, the appearances of the phrases such as "in one or more embodiments," "in certain embodiments," "in one embodiment" or "in an embodiment" in various places throughout this specification are not necessarily referring to the same embodiment of the invention. Furthermore, the particular features, structures, materials, or characteristics may be combined in any suitable manner in one or more embodiments. The order of description of the above method should not be considered limiting, and methods may use the described operations out of order or with omissions or additions.
[0078] It is to be understood that the above description is intended to be illustrative, and not restrictive. Many other embodiments will be apparent to those of ordinary skill in the art upon reviewing the above description. The scope of the invention should, therefore, be determined with reference to the appended claims, along with the full scope of equivalents to which such claims are entitled.
Claims (13)
1. A catalyst comprising:
ceria-alumina composite particles having a ceria phase present in a weight percent of the composite in the range of 20 % to 80% on an oxide basis, an alkaline earth metal component comprising a barium component supported on the ceria-alumina composite particles and present in an amount in the range of 5.0 to 30% by weight on an oxide basis, wherein the Ce02 is present in the form of crystallites that are hydrothermally stable and have an average crystallite size as determined by XRD of less than 160A after aging at 950 C for 5 hours in 2% 02 and 10% steam in I=12.
ceria-alumina composite particles having a ceria phase present in a weight percent of the composite in the range of 20 % to 80% on an oxide basis, an alkaline earth metal component comprising a barium component supported on the ceria-alumina composite particles and present in an amount in the range of 5.0 to 30% by weight on an oxide basis, wherein the Ce02 is present in the form of crystallites that are hydrothermally stable and have an average crystallite size as determined by XRD of less than 160A after aging at 950 C for 5 hours in 2% 02 and 10% steam in I=12.
2. The catalyst of claim 1, wherein the barium component is selected from the group consisting of barium oxide and barium carbonate.
3. The catalyst of claim 1 or 2, wherein the ceria-alumina composite particles contains ceria in an amount in the range of about 30 to 80% by weight on an oxide basis.
4. The catalyst of claim 1 or 2, wherein the ceria-alumina composite particles contains ceria in an amount in the range of about 50 to 80% by weight on an oxide basis.
5. The catalyst of any one of claims 1 to 4, further comprising at least one platinum group metal selected from the group consisting of platinum, palladium, rhodium, iridium, and mixtures thereof, supported on the ceria-alumina composite particles.
6. The catalyst of claim 5, wherein the platinum group metal is selected from the group consisting of platinum, palladium, rhodium, and mixtures thereof.
Date Recue/Date Received 2022-11-08
Date Recue/Date Received 2022-11-08
7. The catalyst of claim 5 or 6, wherein the platinum group metal consists essentially of platinum and palladium.
8. The catalyst of claim 5 or 6, wherein the platinum group metal consists essentially of platinum.
9. The catalyst of any one of claims 1 to 8, wherein the catalyst is selected from the group consisting of a three-way catalyst (TWC), diesel oxidation catalyst (DOC), gasoline particulate filter (GPF), lean NOx trap (LNT), integrated lean NOx trap-three way catalyst (LNT-TWC), and ammonia oxidation (AMOX).
10. A system comprising the catalyst as defined in any one of claims 1 to 9 and a lean burn engine upstream from the catalyst.
11. The system of claim 10 further comprising a second catalyst.
12. The system of claim 11, wherein the second catalyst is selected from the group consisting of a three-way catalyst (TWC), gasoline particulate filter (GPF), selective catalytic reduction (SCR), lean NOx trap (LNT), ammonia oxidation (AMOX), SCR
on a filter (SCRoF), and combinations thereof.
on a filter (SCRoF), and combinations thereof.
13. The system of any one of claims 10 to 12, further comprising a particulate filter.
Date Regue/Date Received 2022-11-08
Date Regue/Date Received 2022-11-08
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BR112020017344A2 (en) * | 2018-02-26 | 2020-12-15 | Basf Corporation | CATALYSTS, BACKGROUND TREATMENT CATALYST, CATALYST PREPARATION PROCESS, TREATMENT METHODS AND PURIFICATION SYSTEM |
US11897779B2 (en) | 2018-08-24 | 2024-02-13 | East China Normal University | Microporous aluminotitanosilicate crystalline zeolite, method of preparation and applications thereof |
KR20220095236A (en) * | 2019-11-12 | 2022-07-06 | 바스프 코포레이션 | particulate filter |
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JP2537239B2 (en) * | 1987-08-28 | 1996-09-25 | エヌ・イーケムキヤツト 株式会社 | Exhaust gas purification catalyst for internal combustion engine excellent in heat resistance and method for producing the same |
JP3285857B2 (en) * | 1989-07-06 | 2002-05-27 | マツダ株式会社 | Exhaust gas purification catalyst |
US5064803A (en) * | 1990-08-31 | 1991-11-12 | Allied-Signal Inc. | Preparation of three-way catalysts with highly dispersed ceria |
US6348430B1 (en) * | 1997-06-20 | 2002-02-19 | Degussa Ag | Exhaust gas treatment catalyst for internal combustion engines with two catalytically active layers on a carrier structure |
US6221804B1 (en) * | 1998-01-27 | 2001-04-24 | Mazda Motor Corporation | Catalyst for purifying exhaust gas and manufacturing method thereof |
US6296822B1 (en) * | 2000-03-29 | 2001-10-02 | Ford Global Technologies, Inc | Process for manufacturing nox traps with improved sulfur tolerance |
US20080120970A1 (en) * | 2006-11-29 | 2008-05-29 | Marcus Hilgendorff | NOx Storage Materials and Traps Resistant to Thermal Aging |
BRPI0916334B1 (en) * | 2008-07-31 | 2019-10-15 | Basf Se | NITROGEN OXIDE STORAGE CATALYST, TREATMENT SYSTEM AND METHOD FOR AN AUTOMOBILE EXHAUST GAS CURRENT, AND METHOD FOR PRODUCING A NITROGEN Oxide STORAGE CATALYST |
JP5768474B2 (en) | 2011-04-28 | 2015-08-26 | 日産自動車株式会社 | Exhaust gas purification system |
JP5806131B2 (en) * | 2012-01-20 | 2015-11-10 | エヌ・イーケムキャット株式会社 | NOx storage denitration catalyst |
WO2014164876A1 (en) * | 2013-03-13 | 2014-10-09 | Basf Corporation | Nox storage catalyst with improved hydrothermal stability and nox conversion |
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2015
- 2015-08-25 EP EP15835062.9A patent/EP3186003A4/en active Pending
- 2015-08-25 BR BR112017002085A patent/BR112017002085A2/en not_active IP Right Cessation
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- 2015-08-25 JP JP2017511323A patent/JP6785755B2/en active Active
- 2015-08-25 MX MX2017002502A patent/MX2017002502A/en unknown
- 2015-08-25 KR KR1020177004943A patent/KR102369734B1/en active IP Right Grant
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EP3186003A4 (en) | 2017-08-30 |
CN106794447A (en) | 2017-05-31 |
JP6785755B2 (en) | 2020-11-18 |
CA2955817A1 (en) | 2016-03-03 |
BR112017002085A2 (en) | 2018-01-30 |
EP3186003A1 (en) | 2017-07-05 |
WO2016033046A1 (en) | 2016-03-03 |
MX2017002502A (en) | 2017-05-23 |
JP2017530859A (en) | 2017-10-19 |
ZA201701901B (en) | 2021-06-30 |
KR102369734B1 (en) | 2022-03-04 |
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