JP5864444B2 - Exhaust gas purification catalyst and exhaust gas purification catalyst structure - Google Patents
Exhaust gas purification catalyst and exhaust gas purification catalyst structure Download PDFInfo
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- JP5864444B2 JP5864444B2 JP2012551833A JP2012551833A JP5864444B2 JP 5864444 B2 JP5864444 B2 JP 5864444B2 JP 2012551833 A JP2012551833 A JP 2012551833A JP 2012551833 A JP2012551833 A JP 2012551833A JP 5864444 B2 JP5864444 B2 JP 5864444B2
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- 239000003054 catalyst Substances 0.000 title claims description 85
- 238000000746 purification Methods 0.000 title claims description 31
- 229910009580 YMnO Inorganic materials 0.000 claims description 39
- BTVJMZJWDVRDMT-UHFFFAOYSA-N dioxido(dioxo)manganese yttrium(3+) Chemical compound [Y+3].[Y+3].[O-][Mn]([O-])(=O)=O.[O-][Mn]([O-])(=O)=O.[O-][Mn]([O-])(=O)=O BTVJMZJWDVRDMT-UHFFFAOYSA-N 0.000 claims description 23
- 239000000919 ceramic Substances 0.000 claims description 10
- 239000007769 metal material Substances 0.000 claims description 7
- 239000002245 particle Substances 0.000 claims description 7
- 239000007789 gas Substances 0.000 description 73
- 230000000052 comparative effect Effects 0.000 description 13
- 238000010304 firing Methods 0.000 description 13
- 229940100890 silver compound Drugs 0.000 description 12
- 150000003379 silver compounds Chemical class 0.000 description 12
- 238000004519 manufacturing process Methods 0.000 description 11
- 239000000843 powder Substances 0.000 description 10
- 238000002485 combustion reaction Methods 0.000 description 8
- SQGYOTSLMSWVJD-UHFFFAOYSA-N silver(1+) nitrate Chemical compound [Ag+].[O-]N(=O)=O SQGYOTSLMSWVJD-UHFFFAOYSA-N 0.000 description 8
- 239000000243 solution Substances 0.000 description 7
- 239000004071 soot Substances 0.000 description 7
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 6
- 239000011572 manganese Substances 0.000 description 6
- 229910052760 oxygen Inorganic materials 0.000 description 6
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 5
- 239000013078 crystal Substances 0.000 description 5
- 239000000203 mixture Substances 0.000 description 5
- 239000001301 oxygen Substances 0.000 description 5
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Substances [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 5
- 239000002904 solvent Substances 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- 239000004215 Carbon black (E152) Substances 0.000 description 4
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 4
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 4
- 229910002091 carbon monoxide Inorganic materials 0.000 description 4
- 238000001035 drying Methods 0.000 description 4
- 229930195733 hydrocarbon Natural products 0.000 description 4
- 150000002430 hydrocarbons Chemical class 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- KDLHZDBZIXYQEI-UHFFFAOYSA-N palladium Substances [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 description 4
- 229910001961 silver nitrate Inorganic materials 0.000 description 4
- 239000002002 slurry Substances 0.000 description 4
- 239000011248 coating agent Substances 0.000 description 3
- 238000000576 coating method Methods 0.000 description 3
- 238000000635 electron micrograph Methods 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- 229910052709 silver Inorganic materials 0.000 description 3
- 239000004332 silver Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- NGDQQLAVJWUYSF-UHFFFAOYSA-N 4-methyl-2-phenyl-1,3-thiazole-5-sulfonyl chloride Chemical compound S1C(S(Cl)(=O)=O)=C(C)N=C1C1=CC=CC=C1 NGDQQLAVJWUYSF-UHFFFAOYSA-N 0.000 description 2
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 2
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- 239000007864 aqueous solution Substances 0.000 description 2
- 239000011230 binding agent Substances 0.000 description 2
- 239000000969 carrier Substances 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 229910052878 cordierite Inorganic materials 0.000 description 2
- 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 2
- 230000000694 effects Effects 0.000 description 2
- 239000007791 liquid phase Substances 0.000 description 2
- 238000005259 measurement Methods 0.000 description 2
- 229910017604 nitric acid Inorganic materials 0.000 description 2
- 229910000510 noble metal Inorganic materials 0.000 description 2
- 230000001590 oxidative effect Effects 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- NDVLTYZPCACLMA-UHFFFAOYSA-N silver oxide Chemical compound [O-2].[Ag+].[Ag+] NDVLTYZPCACLMA-UHFFFAOYSA-N 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- ZXSQEZNORDWBGZ-UHFFFAOYSA-N 1,3-dihydropyrrolo[2,3-b]pyridin-2-one Chemical compound C1=CN=C2NC(=O)CC2=C1 ZXSQEZNORDWBGZ-UHFFFAOYSA-N 0.000 description 1
- 229910002060 Fe-Cr-Al alloy Inorganic materials 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- ODUCDPQEXGNKDN-UHFFFAOYSA-N Nitrogen oxide(NO) Natural products O=N ODUCDPQEXGNKDN-UHFFFAOYSA-N 0.000 description 1
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- 229910021607 Silver chloride Inorganic materials 0.000 description 1
- 229910010413 TiO 2 Inorganic materials 0.000 description 1
- GEIAQOFPUVMAGM-UHFFFAOYSA-N ZrO Inorganic materials [Zr]=O GEIAQOFPUVMAGM-UHFFFAOYSA-N 0.000 description 1
- XHCLAFWTIXFWPH-UHFFFAOYSA-N [O-2].[O-2].[O-2].[O-2].[O-2].[V+5].[V+5] Chemical compound [O-2].[O-2].[O-2].[O-2].[O-2].[V+5].[V+5] XHCLAFWTIXFWPH-UHFFFAOYSA-N 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- IXSUHTFXKKBBJP-UHFFFAOYSA-L azanide;platinum(2+);dinitrite Chemical compound [NH2-].[NH2-].[Pt+2].[O-]N=O.[O-]N=O IXSUHTFXKKBBJP-UHFFFAOYSA-L 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 description 1
- 229910000420 cerium oxide Inorganic materials 0.000 description 1
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910052809 inorganic oxide Inorganic materials 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- MIVBAHRSNUNMPP-UHFFFAOYSA-N manganese(2+);dinitrate Chemical compound [Mn+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O MIVBAHRSNUNMPP-UHFFFAOYSA-N 0.000 description 1
- YMKHJSXMVZVZNU-UHFFFAOYSA-N manganese(2+);dinitrate;hexahydrate Chemical compound O.O.O.O.O.O.[Mn+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O YMKHJSXMVZVZNU-UHFFFAOYSA-N 0.000 description 1
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 description 1
- 238000000691 measurement method Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 150000002823 nitrates Chemical class 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- BMMGVYCKOGBVEV-UHFFFAOYSA-N oxo(oxoceriooxy)cerium Chemical compound [Ce]=O.O=[Ce]=O BMMGVYCKOGBVEV-UHFFFAOYSA-N 0.000 description 1
- RVTZCBVAJQQJTK-UHFFFAOYSA-N oxygen(2-);zirconium(4+) Chemical compound [O-2].[O-2].[Zr+4] RVTZCBVAJQQJTK-UHFFFAOYSA-N 0.000 description 1
- 229910052763 palladium Inorganic materials 0.000 description 1
- GPNDARIEYHPYAY-UHFFFAOYSA-N palladium(ii) nitrate Chemical compound [Pd+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O GPNDARIEYHPYAY-UHFFFAOYSA-N 0.000 description 1
- 239000013618 particulate matter Substances 0.000 description 1
- 238000011056 performance test Methods 0.000 description 1
- 229910052697 platinum Inorganic materials 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000010970 precious metal Substances 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 229910052703 rhodium Inorganic materials 0.000 description 1
- 239000010948 rhodium Substances 0.000 description 1
- CQLFBEKRDQMJLZ-UHFFFAOYSA-M silver acetate Chemical compound [Ag+].CC([O-])=O CQLFBEKRDQMJLZ-UHFFFAOYSA-M 0.000 description 1
- 229940071536 silver acetate Drugs 0.000 description 1
- LKZMBDSASOBTPN-UHFFFAOYSA-L silver carbonate Substances [Ag].[O-]C([O-])=O LKZMBDSASOBTPN-UHFFFAOYSA-L 0.000 description 1
- 229910001958 silver carbonate Inorganic materials 0.000 description 1
- 229940096017 silver fluoride Drugs 0.000 description 1
- HKZLPVFGJNLROG-UHFFFAOYSA-M silver monochloride Chemical compound [Cl-].[Ag+] HKZLPVFGJNLROG-UHFFFAOYSA-M 0.000 description 1
- REYHXKZHIMGNSE-UHFFFAOYSA-M silver monofluoride Chemical compound [F-].[Ag+] REYHXKZHIMGNSE-UHFFFAOYSA-M 0.000 description 1
- 229960001516 silver nitrate Drugs 0.000 description 1
- 229910001923 silver oxide Inorganic materials 0.000 description 1
- AYKOTYRPPUMHMT-UHFFFAOYSA-N silver;hydrate Chemical compound O.[Ag] AYKOTYRPPUMHMT-UHFFFAOYSA-N 0.000 description 1
- 229910001256 stainless steel alloy Inorganic materials 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 239000002344 surface layer Substances 0.000 description 1
- 229910001935 vanadium oxide Inorganic materials 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
- 229910052727 yttrium Inorganic materials 0.000 description 1
- QBAZWXKSCUESGU-UHFFFAOYSA-N yttrium(3+);trinitrate;hexahydrate Chemical compound O.O.O.O.O.O.[Y+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O QBAZWXKSCUESGU-UHFFFAOYSA-N 0.000 description 1
- 229910001928 zirconium oxide Inorganic materials 0.000 description 1
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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
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- 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
- B01J23/66—Silver or gold
- B01J23/68—Silver or gold with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J23/688—Silver or gold with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium with manganese, technetium or rhenium
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- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/50—Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
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- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/02—Impregnation, coating or precipitation
- B01J37/03—Precipitation; Co-precipitation
- B01J37/038—Precipitation; Co-precipitation to form slurries or suspensions, e.g. a washcoat
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- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/16—Reducing
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- B01D2255/915—Catalyst supported on particulate filters
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- Catalysts (AREA)
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- Exhaust Gas After Treatment (AREA)
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Description
本発明は自動車等の内燃機関から排出される排気ガスを浄化するために使用される排気ガス浄化用触媒及び排気ガス浄化用触媒構成体に関する。 The present invention relates to an exhaust gas purifying catalyst and an exhaust gas purifying catalyst structure used for purifying exhaust gas discharged from an internal combustion engine such as an automobile.
自動車等の内燃機関から排出される排ガス中には、炭化水素(HC)、一酸化炭素(CO)、窒素酸化物(NO)等の有害成分が含まれている。それで、従来から、これら有害成分を浄化して無害化する三元触媒が用いられている。 In exhaust gas discharged from an internal combustion engine such as an automobile, harmful components such as hydrocarbon (HC), carbon monoxide (CO), and nitrogen oxide (NO) are contained. Therefore, conventionally, a three-way catalyst for purifying and detoxifying these harmful components has been used.
このような三元触媒として、Pt、Pd、Rh等の貴金属とアルミナ、セリア、ジルコニア又はこれらの複合酸化物とを任意に組み合わせて、セラミックス又は金属等のハニカム担体上に塗布させたものが使用されている。 As such a three-way catalyst, a precious metal such as Pt, Pd, Rh, etc. and any combination of alumina, ceria, zirconia, or a composite oxide thereof applied to a honeycomb carrier such as ceramic or metal is used. Has been.
また、ディーゼルエンジンから排出される排気ガスはパティキュレート(粒子状物質)を含んでおり、これらの物質がそのまま大気中に放出されると大気汚染の原因になる。パティキュレートを取り除くための有効な手段として、ススを捕集するためのディーゼル・パティキュレート・フィルター(DPF)を用いたディーゼル排ガストラップシステムがある。しかし、このDPFでは捕集したパティキュレートを酸化除去してDPFを再生する必要がある。 Further, the exhaust gas discharged from the diesel engine contains particulates (particulate matter), and if these materials are released into the atmosphere as they are, they cause air pollution. As an effective means for removing particulates, there is a diesel exhaust gas trap system using a diesel particulate filter (DPF) for collecting soot. However, in this DPF, it is necessary to regenerate the DPF by oxidizing and removing the collected particulates.
これまでに提案されたシステムとしては、担体、例えば、酸化ジルコニウム、酸化バナジウム、酸化セリウム等の無機酸化物からなる担体にPtなどの高価な貴金属を担持させた触媒(例えば、特許文献1、2及び3参照)や、安価な銀を担持させて触媒を用いるシステムがある。また、従来、銀を用いるものは安価であるものの、耐熱性に劣ることが指摘されている(非特許文献1参照)。 As a system proposed so far, a catalyst (for example, Patent Documents 1 and 2) in which an expensive noble metal such as Pt is supported on a support, for example, a support made of an inorganic oxide such as zirconium oxide, vanadium oxide, or cerium oxide. And 3) and a system that uses a catalyst by supporting inexpensive silver. Conventionally, it has been pointed out that although silver is inexpensive, it is inferior in heat resistance (see Non-Patent Document 1).
本発明は自動車等の内燃機関から排出される排気ガスに対して有害なガス成分を浄化し且つパティキュレートを酸化除去し得る排気ガス浄化用触媒及び排気ガス浄化用触媒構成体を提供することを目的としている。 The present invention provides an exhaust gas purification catalyst and an exhaust gas purification catalyst structure capable of purifying gas components harmful to exhaust gas discharged from an internal combustion engine such as an automobile and oxidizing and removing particulates. It is aimed.
本発明者らは上記の目的を達成するために種々の物質の組み合わせを用いて種々の実験を行った結果、マンガン酸イットリウムYMnO3にAgを担持させることにより優れた排気ガス浄化性能とAgの欠点であった熱耐久性の問題も克服されることを見出し、本発明を完成した。As a result of various experiments using various combinations of substances in order to achieve the above-mentioned object, the present inventors have achieved excellent exhaust gas purification performance and Ag by supporting Ag on yttrium manganate YMnO 3 . The present inventors have found that the problem of heat durability, which has been a drawback, can also be overcome.
即ち、本発明の排気ガス浄化用触媒は、マンガン酸イットリウムYMnO3を含む担体と、該担体の表面上に担持されているAgとからなることを特徴とする。That is, the exhaust gas purifying catalyst of the present invention comprises a carrier containing yttrium manganate YMnO 3 and Ag supported on the surface of the carrier.
本発明の排気ガス浄化用触媒においては、Agの担持量がYの原子数を基準にして1〜10at%であることが好ましく、4〜9at%であることが一層好ましい。 In the exhaust gas purifying catalyst of the present invention, the supported amount of Ag is preferably 1 to 10 at%, more preferably 4 to 9 at%, based on the number of Y atoms.
また、本発明の排気ガス浄化用触媒構成体は、セラミックス又は金属材料からなる触媒支持体と、該触媒支持体上に担持されている上記の排気ガス浄化用触媒とを備えていることを特徴とする。 The exhaust gas purifying catalyst component of the present invention comprises a catalyst support made of a ceramic or metal material and the exhaust gas purifying catalyst supported on the catalyst support. And
本発明の排気ガス浄化用触媒構成体においては、セラミックス又は金属材料からなる触媒支持体がハニカム形状であるか、又はDPFであることが好ましい。 In the exhaust gas purifying catalyst structure of the present invention, it is preferable that the catalyst support made of ceramics or a metal material has a honeycomb shape or a DPF.
本発明の排気ガス浄化用触媒及び排気ガス浄化用触媒構成体は自動車等の内燃機関から排出される排気ガスに対して有害なガス成分を浄化し且つパティキュレートを酸化除去し得るので、即ち排気ガス浄化性能に優れているので、自動車等の内燃機関から排出される排気ガスを浄化するのに有効である。 The exhaust gas purifying catalyst and the exhaust gas purifying catalyst structure of the present invention can purify gas components harmful to exhaust gas discharged from an internal combustion engine such as an automobile and oxidize and remove particulates. Since the gas purification performance is excellent, it is effective for purifying exhaust gas discharged from an internal combustion engine such as an automobile.
以下に、本発明の排気ガス浄化用触媒及び排気ガス浄化用触媒構成体について具体的に説明する。 Hereinafter, the exhaust gas purifying catalyst and the exhaust gas purifying catalyst structure of the present invention will be described in detail.
本発明の排気ガス浄化用触媒及び排気ガス浄化用触媒構成体で用いるマンガン酸イットリウムは化学式YMnO3で表わされる公知の複酸化物であり、この複酸化物YMnO3は、例えば、硝酸イットリウムと硝酸マンガンとクエン酸と水とからなる混合物を、200〜400℃の範囲内の温度、1〜10時間の範囲内の時間で一次焼成し、次いで800〜1000℃の範囲内の温度、1〜10時間の範囲内の時間で二次焼成することにより製造することができる。Yttrium manganate used in the exhaust gas purifying catalyst and the exhaust gas purifying catalyst structure of the present invention is a known double oxide represented by the chemical formula YMnO 3 , and this double oxide YMnO 3 includes, for example, yttrium nitrate and nitric acid. A mixture of manganese, citric acid and water is first calcined at a temperature in the range of 200-400 ° C. for a time in the range of 1-10 hours, and then at a temperature in the range of 800-1000 ° C., 1-10. It can manufacture by carrying out secondary baking for the time within the range of time.
上記の複酸化物YMnO3の製造方法においては、例えば、硝酸イットリウム6水和物と硝酸マンガン6水和物とクエン酸と水とを1:1:6:40のモル比の混合物として用いることができる。上記の製造方法において硝酸イットリウムと硝酸マンガンとのモル比が1:1からずれた場合や、反応温度、反応時間等の反応条件の変化によっては副生物として複酸化物YMn2O5、複酸化物Y2Mn2O7、Y2O3、Mn2O3が生じることがあるが、これらの副生物を含む混合物も本発明において担体として同様に有用である。従って、本発明においてはマンガン酸イットリウムYMnO3を含む担体と表示する。また、上記の複酸化物YMnO3の製造方法で得られるYMnO3の結晶系は六方晶、斜方晶又はこれらの混合の形の何れかになるが、何れのものも本発明において担体として有用である。
In the above method for producing the double oxide YMnO 3 , for example, yttrium nitrate hexahydrate, manganese nitrate hexahydrate, citric acid and water are used as a mixture in a molar ratio of 1: 1: 6: 40. Can do. In the above production method, when the molar ratio of yttrium nitrate to manganese nitrate deviates from 1: 1, or depending on changes in reaction conditions such as reaction temperature and reaction time, double oxide YMn 2 O 5 , double oxidation The products Y 2 Mn 2 O 7 , Y 2 O 3 , Mn 2 O 3 may be produced, but mixtures containing these by-products are also useful as carriers in the present invention. Therefore, in the present invention, it is expressed as a support containing yttrium manganate YMnO 3 . Further, the crystal system of YMnO 3 obtained by the above-described method for producing the double oxide YMnO 3 is in the form of hexagonal crystal, orthorhombic crystal or a mixture thereof, any of which is useful as a support in the present invention. It is.
また、他の製造方法としては、原料としてY2O3及びMnO2をY/Mnの原子比が1/1になるように秤取し、例えばボールミルを用いて3時間以上粉砕・混合する方法を挙げることができる。この方法では、その後大気雰囲気下、900℃で5時間焼成することにより複酸化物YMnO3を得ることができる。As another production method, Y 2 O 3 and MnO 2 as raw materials are weighed so that the atomic ratio of Y / Mn is 1/1, and pulverized and mixed for 3 hours or more using, for example, a ball mill Can be mentioned. In this method, the double oxide YMnO 3 can be obtained by firing at 900 ° C. for 5 hours in the air atmosphere.
さらに、他の製造方法としては、液相法を挙げることができる。例えば、液相法では、原料としてY、Mnの硝酸塩をY/Mnの原子比が1/1になる様に秤取し、水溶液としたものに、アンモニア等のアルカリ水溶液を滴下してYとMnの沈殿を作り、これを濾過、洗浄、乾燥後例えば800℃程度の十分な加熱により硝酸根を除去・結晶化することで複酸化物YMnO3を得ることができる。 Furthermore, as another manufacturing method, a liquid phase method can be mentioned. For example, in the liquid phase method, nitrates of Y and Mn as raw materials are weighed so that the atomic ratio of Y / Mn becomes 1/1, and an aqueous solution such as ammonia is dropped into an aqueous solution. A double oxide YMnO 3 can be obtained by making a precipitate of Mn, filtering, washing and drying, and removing and crystallizing nitrate radicals by sufficient heating, for example, at about 800 ° C.
何れにしても、複酸化物YMnO3の製造方法は特に限定されるものではない。In any case, the method for producing the double oxide YMnO 3 is not particularly limited.
本発明の排気ガス浄化用触媒は、このようなマンガン酸イットリウムYMnO3を含む担体にAgを担持させたものである。担体はYMnO3を単独で用いたものでもよく、アルミナ(Al2O3)、CeO2、(CeZr)O2など他の公知の担体と混合して用いてもよい。The exhaust gas purifying catalyst of the present invention is such that Ag is supported on a carrier containing such yttrium manganate YMnO 3 . The carrier may be YMnO 3 used alone, or may be used by mixing with other known carriers such as alumina (Al 2 O 3 ), CeO 2 , (CeZr) O 2 .
マンガン酸イットリウムYMnO3を含む担体と、該担体の表面上に担持されているAgとからなる本発明の排気ガス浄化用触媒は、例えば、可溶性銀化合物の溶液中に、マンガン酸イットリウムYMnO3からなる担体粉末を入れて撹拌し、そのスラリーを加熱乾燥し、焼成することにより製造することができる。また、別の製法として、マンガン酸イットリウムYMnO3からなる担体粉末とAg粉末又は炭酸銀等のAg化合物粉末とを配合し、焼成することにより製造することもできる。それらの焼成雰囲気として、例えば空気、酸素富化空気を用いることができ、また焼成を例えば450〜600℃で実施することができる。その際、銀の一部が、YMnO3の結晶の格子内に含有されるか又は結晶に固溶していることもあり得る。The exhaust gas purifying catalyst of the present invention comprising a carrier containing yttrium manganate YMnO 3 and Ag supported on the surface of the carrier is, for example, from yttrium manganate YMnO 3 in a solution of a soluble silver compound. It can be manufactured by adding the carrier powder to be stirred and drying and baking the slurry. As another production method, a carrier powder composed of yttrium manganate YMnO 3 and an Ag compound powder such as Ag powder or silver carbonate can be blended and fired. As the firing atmosphere, for example, air or oxygen-enriched air can be used, and firing can be performed at 450 to 600 ° C., for example. At that time, a part of silver may be contained in the crystal lattice of YMnO 3 or may be dissolved in the crystal.
また、セラミックス又は金属材料からなる触媒支持体と、該触媒支持体表面に担持されている上記の排気ガス浄化用触媒とを備えている本発明の排気ガス浄化用触媒構成体は、例えば、可溶性銀化合物の溶液中に、マンガン酸イットリウムYMnO3からなる担体紛体を入れて撹拌し、そのスラリーをセラミックス又は金属材料からなるハニカム形状又はDPFである触媒支持体表面にコートさせ、その後乾燥し、焼成することにより製造することができる。焼成雰囲気として、例えば空気、酸素富化空気を用いることができ、また焼成を例えば450〜600℃で実施することができる。The exhaust gas purifying catalyst component of the present invention comprising a catalyst support made of ceramics or a metal material and the exhaust gas purifying catalyst supported on the surface of the catalyst support is, for example, soluble A carrier powder made of yttrium manganate YMnO 3 is placed in a silver compound solution and stirred. The slurry is coated on the surface of a catalyst support made of a ceramic or metal material in the form of a honeycomb or DPF, and then dried and fired. Can be manufactured. As the firing atmosphere, for example, air or oxygen-enriched air can be used, and firing can be performed at 450 to 600 ° C., for example.
あるいは、セラミックス又は金属材料からなる触媒支持体と、該触媒支持体表面に担持されている上記の排気ガス浄化用触媒とを備えている本発明の排気ガス浄化用触媒構成体は、例えば、セラミックス又は金属材料からなる触媒支持体表面にマンガン酸イットリウムYMnO3からなる担体紛体を担持させ、該担体紛体を担持した触媒支持体に可溶性銀化合物の溶液を接触させ、その後乾燥し、焼成することにより製造することもできる。焼成雰囲気として、例えば空気、酸素富化空気を用いることができ、また焼成を例えば450〜600℃で実施することができる。Alternatively, the exhaust gas purifying catalyst component of the present invention comprising a catalyst support made of ceramics or a metal material and the exhaust gas purifying catalyst supported on the surface of the catalyst support is, for example, a ceramic. Alternatively, a carrier powder made of yttrium manganate YMnO 3 is supported on the surface of a catalyst support made of a metal material, a solution of a soluble silver compound is brought into contact with the catalyst support carrying the carrier powder, and then dried and calcined. It can also be manufactured. As the firing atmosphere, for example, air or oxygen-enriched air can be used, and firing can be performed at 450 to 600 ° C., for example.
上記の製造方法において可溶性銀化合物の溶液を用いる場合には、可溶性銀化合物及び該銀化合物を溶解する溶媒を用いる。例えば、銀化合物として硝酸銀、酢酸銀、フッ化銀等を用いる場合には溶媒として水等を用いることができ、銀化合物として酸化銀等を用いる場合には溶媒として硝酸、アンモニア水等を用いることができ、銀化合物として塩化銀等を用いる場合には溶媒としてアンモニア水等を用いることができ、可溶性銀化合物と溶媒との組み合わせは当業者には自明である。 When using the solution of a soluble silver compound in said manufacturing method, the solvent which melt | dissolves a soluble silver compound and this silver compound is used. For example, when silver nitrate, silver acetate, silver fluoride or the like is used as the silver compound, water or the like can be used as the solvent, and when silver oxide or the like is used as the silver compound, nitric acid, aqueous ammonia or the like is used as the solvent. When silver chloride or the like is used as the silver compound, aqueous ammonia or the like can be used as the solvent, and the combination of the soluble silver compound and the solvent is obvious to those skilled in the art.
本発明の排気ガス浄化用触媒及び排気ガス浄化用触媒構成体において、マンガン酸イットリウムYMnO3を含む担体の表面上に担持されているAg粒子については、10〜20nmの大きさのものを含むことが好ましい。すなわち、Ag粒子が10nm以上であるとマンガン酸イットリウムYMnO3粒子の細孔に入りにくく、20nm以下であるとYMnO3と良好な接触を保ち効果的だからである。In the exhaust gas purifying catalyst and exhaust gas purifying catalyst structure of the present invention, the Ag particles supported on the surface of the carrier containing yttrium manganate YMnO 3 include those having a size of 10 to 20 nm. Is preferred. That is, if the Ag particle is 10 nm or more, it is difficult to enter the pores of the yttrium manganate YMnO 3 particle, and if it is 20 nm or less, good contact with YMnO 3 is maintained and effective.
本発明の排気ガス浄化用触媒構成体、特にDPFを製造することを考慮すると、担体の表面にバインダー成分としてSiO2、TiO2、ZrO2、Al2O3などを付与しておくことが好ましい。担体の表面にバインダー成分を付与することにより基材と担体との密着性が向上して触媒の耐久性が向上し、耐熱性が向上する。Considering the production of the exhaust gas purifying catalyst structure of the present invention, particularly the DPF, it is preferable to give SiO 2 , TiO 2 , ZrO 2 , Al 2 O 3 or the like as a binder component to the surface of the carrier. . By applying a binder component to the surface of the carrier, the adhesion between the substrate and the carrier is improved, the durability of the catalyst is improved, and the heat resistance is improved.
DPFはDPFとして公知のいかなる形状であっても良いが、三次元立体構造を有するものが好ましい。三次元立体構造を有するフィルターの具体例として、ウォールスルー型、フロースルーハニカム型、ワイヤメッシュ型、セラミックファイバー型、金属多孔体型、粒子充填型、フォーム型等を挙げることができる。また、基材の材質としてコージエライト、SiCなどのセラミックやFe−Cr−Al合金やステンレス合金などを挙げることができる。触媒の総コート量としては、ウォールスルー型DPFの場合には10〜100g/L、ワイヤメッシュ型の場合には50〜150g/Lくらいが好ましい。触媒の総コート量が少なすぎると充分な性能を得ることができない。また、多すぎると排ガスに対する背圧が高くなってしまう。なお、ウォールスルー型DPFの場合には触媒はウォール内部の間隙に入り込まず表層のみに堆積した状態であることが好ましい。 The DPF may have any shape known as DPF, but preferably has a three-dimensional structure. Specific examples of the filter having a three-dimensional structure include a wall-through type, a flow-through honeycomb type, a wire mesh type, a ceramic fiber type, a metal porous body type, a particle filling type, and a foam type. Further, examples of the material of the base material include cordierite, SiC and other ceramics, Fe—Cr—Al alloys, stainless steel alloys, and the like. The total coating amount of the catalyst is preferably about 10 to 100 g / L for the wall-through type DPF and about 50 to 150 g / L for the wire mesh type. If the total coating amount of the catalyst is too small, sufficient performance cannot be obtained. Moreover, when there is too much, the back pressure with respect to waste gas will become high. In the case of a wall-through type DPF, the catalyst is preferably in a state where it is deposited only on the surface layer without entering the gap inside the wall.
本発明の排気ガス浄化用触媒構成体を三次元構造のDPFとして製造する場合には、可溶性銀化合物の溶液中にマンガン酸イットリウムYMnO3からなる担体紛体を入れて撹拌し、そのスラリーを三次元構造のDPFである触媒支持体にコートさせ、その後乾燥し、焼成することにより製造することができる。焼成雰囲気として、例えば空気、酸素富化空気を用いることができ、また焼成を例えば450〜600℃で実施することができる。When the exhaust gas purifying catalyst component of the present invention is produced as a three-dimensional DPF, a carrier powder composed of yttrium manganate YMnO 3 is put in a solution of a soluble silver compound and stirred, and the slurry is three-dimensional. It can be produced by coating a catalyst support, which is a DPF having a structure, followed by drying and firing. As the firing atmosphere, for example, air or oxygen-enriched air can be used, and firing can be performed at 450 to 600 ° C., for example.
本発明の排気ガス浄化用触媒構成体を三次元構造のDPFとして製造するその他の方法として、三次元構造のDPFである触媒支持体にマンガン酸イットリウムYMnO3からなる担体紛体を担持させ、該担体紛体を担持した触媒支持体に可溶性銀化合物の溶液を接触させ、その後乾燥し、焼成することにより製造することもできる。それらの焼成雰囲気として、例えば空気、酸素富化空気を用いることができ、また焼成を例えば450〜600℃で実施することができる。As another method for producing the exhaust gas purifying catalyst component of the present invention as a three-dimensional DPF, a carrier support made of yttrium manganate YMnO 3 is supported on a catalyst support which is a three-dimensional DPF, and the carrier It can also be produced by bringing a solution of a soluble silver compound into contact with a catalyst support on which a powder is supported, followed by drying and firing. As the firing atmosphere, for example, air or oxygen-enriched air can be used, and firing can be performed at 450 to 600 ° C., for example.
本発明の排気ガス浄化用触媒及び排気ガス浄化用触媒構成体においては、後記の実施例のデータからも明らかなように、Agの担持量がYの原子数を基準にして1〜10at%であることが好ましく、4〜9at%であることが一層好ましい。Agの担持量が1at%よりも少ない場合には排気ガス浄化性能が不十分であり、また10at%よりも多くなっても排気ガス浄化性能が頭打ちとなる傾向がある。 In the exhaust gas purifying catalyst and the exhaust gas purifying catalyst structure of the present invention, as is clear from the data of the examples described later, the supported amount of Ag is 1 to 10 at% based on the number of Y atoms. Preferably, it is 4-9 at%. When the amount of Ag loaded is less than 1 at%, the exhaust gas purification performance is insufficient, and even when the amount is more than 10 at%, the exhaust gas purification performance tends to reach its peak.
以下に、実施例及び比較例に基づいて本発明を具体的に説明する。 Hereinafter, the present invention will be described in detail based on examples and comparative examples.
実施例1〜5及び比較例1
硝酸銀水溶液中にAgの量がYの原子数を基準にしてそれぞれ第1表に示す割合となるようにマンガン酸イットリウムYMnO3からなる担体粉末を投入し、30分間攪拌した。得られた各々のスラリーを直径25.4mm×長さ76.2mmのコージェライト製パティキュレートフィルター表面にコートさせた。これらを120℃で3時間乾燥した後、空気中500℃で1時間焼成した。得られた各々のパティキュレートフィルター形状の排ガス浄化用触媒構成体のYMnO3の担持量は40g/Lであり、Agの担持量は金属換算で第1表に示す通りであった。なお、実施例5で得た排気ガス浄化用触媒構成体の一部分の電子顕微鏡写真を図1に示す。図1の電子顕微鏡写真において1目盛の長さは6nmであり、10目盛りで60nmであることを示している。図1から明らかなように、YMnO3担体上に担持されているAg粒子の大きさは10〜20nm程度である。Examples 1 to 5 and Comparative Example 1
A carrier powder composed of yttrium manganate YMnO 3 was added to an aqueous silver nitrate solution so that the amount of Ag would be the ratio shown in Table 1 based on the number of Y atoms, and stirred for 30 minutes. Each obtained slurry was coated on the surface of a particulate filter made of cordierite having a diameter of 25.4 mm and a length of 76.2 mm. These were dried at 120 ° C. for 3 hours and then calcined in air at 500 ° C. for 1 hour. In each of the obtained particulate filter-shaped exhaust gas purification catalyst components, the supported amount of YMnO 3 was 40 g / L, and the supported amount of Ag was as shown in Table 1 in terms of metal. An electron micrograph of a part of the exhaust gas purifying catalyst structure obtained in Example 5 is shown in FIG. In the electron micrograph of FIG. 1, the length of one scale is 6 nm, and the scale of 10 is 60 nm. As apparent from FIG. 1, the size of Ag particles supported on the YMnO 3 support is about 10 to 20 nm.
<排ガス浄化性能試験>
実施例1〜5及び比較例1で得られた各々の排気ガス浄化用触媒構成体を大気中、700℃で30時間耐久処理した。耐久処理後の排気ガス浄化用触媒構成体の触媒活性を以下のようにして評価した。<Exhaust gas purification performance test>
Each exhaust gas purifying catalyst structure obtained in Examples 1 to 5 and Comparative Example 1 was subjected to a durability treatment at 700 ° C. for 30 hours in the atmosphere. The catalytic activity of the exhaust gas purifying catalyst structure after the durability treatment was evaluated as follows.
それらの排ガス浄化用触媒構成体を別々にモデルガス測定装置(堀場製作所製MEXA−7500D)に装填し、下記の第2表に示す組成の排気モデルガスを空間速度29000/hで流通させながら、600℃から17℃/分の降温速度で降温させ、CO、HC浄化率を連続的に測定した。得られた測定結果より、CO/HCそれぞれの50%浄化率に到達する温度(T50)を求めた。それらの結果は第1表に示す通りであった。 The exhaust gas purification catalyst components were separately loaded into a model gas measuring device (MEXA-7500D manufactured by Horiba, Ltd.), and the exhaust model gas having the composition shown in Table 2 below was circulated at a space velocity of 29000 / h. The temperature was lowered from 600 ° C. at a rate of 17 ° C./min, and the CO and HC purification rates were measured continuously. From the obtained measurement results, the temperature (T50) at which each CO / HC reached a 50% purification rate was determined. The results were as shown in Table 1.
第1表に示すデータから明らかなように、Agを担持したマンガン酸イットリウムYMnO3を備える本発明の排気ガス浄化用触媒構成体はAgを担持しないマンガン酸イットリウムYMnO3を備える比較例の排気ガス浄化用触媒構成体よりも排気ガス浄化性能に優れており、また、Agの担持量が1〜10at%である場合に十分な排気ガス浄化効果が得られており、特にAgの担持量が4〜9at%である場合に顕著な排気ガス浄化効果が得られている。As is apparent from the data shown in Table 1, the exhaust gas purifying catalyst component of the present invention having yttrium manganate YMnO 3 supporting Ag is an exhaust gas of a comparative example having yttrium manganate YMnO 3 not supporting Ag. The exhaust gas purification performance is superior to that of the purification catalyst structure, and a sufficient exhaust gas purification effect is obtained when the supported amount of Ag is 1 to 10 at%. When it is ˜9 at%, a significant exhaust gas purification effect is obtained.
<スス燃焼速度の測定法>
実施例5で得られたAg/YMnO3担持排気ガス浄化用触媒構成体(Ag担持量2.3g/L)、比較例1で得られたYMnO3担持排気ガス浄化用触媒構成体(貴金属担持なし)、硝酸銀の代わりに硝酸パラジウムを用いた以外は実施例5と同様にして得られたPd/YMnO3担持排気ガス浄化用触媒構成体(Pd担持量0.4g/L)(比較例2)、及び硝酸銀の代わりにジニトロジアンミン白金を用い、YMnO3の代わりにAl2O3を用いた以外は実施例5と同様にして得られたPt/Al2O3担持排気ガス浄化用触媒構成体(Pt担持量0.5g/L)(比較例3)をそれぞれ大気中、700℃で30時間耐久処理した。耐久処理後の各々の排気ガス浄化用触媒構成体について下記の方法でスス燃焼速度を測定した。<Measurement method of soot burning rate>
Ag / YMnO 3 supported exhaust gas purification catalyst structure obtained in Example 5 (Ag supported amount 2.3 g / L), YMnO 3 supported exhaust gas purification catalyst structure obtained in Comparative Example 1 (noble metal support) None), Pd / YMnO 3 -supported exhaust gas purification catalyst structure (Pd support amount 0.4 g / L) obtained in the same manner as in Example 5 except that palladium nitrate was used instead of silver nitrate (Comparative Example 2) And Pt / Al 2 O 3 supported exhaust gas purifying catalyst structure obtained in the same manner as in Example 5 except that dinitrodiammine platinum was used instead of silver nitrate and Al 2 O 3 was used instead of YMnO 3. Each of the bodies (Pt supported amount 0.5 g / L) (Comparative Example 3) was endured for 30 hours at 700 ° C. in the air. The soot combustion rate was measured by the following method for each exhaust gas purifying catalyst structure after the endurance treatment.
2.4Lディーゼルエンジンの排気ガスを上記の排気ガス浄化用触媒構成体中に通してススを排気ガス浄化用触媒構成体1L当たり2g捕集させた。その後、600℃でO2:3.8%、NO:200ppm、残部:N2からなるガスを空間速度(SV)21300/hで流通させてスス燃焼速度を測定した。測定には堀場製作所製MEXA−7500Dを用いた。90%再生時間(捕集されていたススの90%が燃焼するまでの時間)は第3表に示す通りであった。The exhaust gas of the 2.4 L diesel engine was passed through the exhaust gas purification catalyst structure, and 2 g of soot was collected per 1 L of the exhaust gas purification catalyst structure. Thereafter, a soot combustion rate was measured by circulating a gas consisting of O 2 : 3.8%, NO: 200 ppm, and the balance: N 2 at 600 ° C. at a space velocity (SV) of 21300 / h. MEXA-7500D manufactured by Horiba Seisakusho was used for the measurement. The 90% regeneration time (the time until 90% of the collected soot burned) was as shown in Table 3.
第3表に示すデータから明らかなように、Agを担持したマンガン酸イットリウムYMnO3を備える本発明の実施例5の排気ガス浄化用触媒構成体は、Agを担持しないマンガン酸イットリウムYMnO3を備える比較例1の排気ガス浄化用触媒構成体、Pdを担持したマンガン酸イットリウムYMnO3を備える比較例2の排気ガス浄化用触媒構成体、Ptを担持したAl2O3を備える比較例3の排気ガス浄化用触媒構成体よりもスス燃焼速度において優れている。なお、実施例5の排気ガス浄化用触媒構成体のAgの担持量は、比較例2の排気ガス浄化用触媒構成体のPdの担持量及び比較例3の排気ガス浄化用触媒構成体のPtの担持量よりも多いが、実施例5の排気ガス浄化用触媒構成体は比較例2及び3のものよりも安価である。従って、マンガン酸イットリウムYMnO3とAgとを組み合わせることで優れた排気ガス浄化性能と耐熱性を有する触媒が得られることが明らかになった。As is clear from the data shown in Table 3 , the exhaust gas purifying catalyst structure of Example 5 of the present invention including yttrium manganate YMnO 3 supporting Ag is provided with yttrium manganate YMnO 3 not supporting Ag. Exhaust gas purification catalyst structure of Comparative Example 1, Exhaust gas purification catalyst structure of Comparative Example 2 comprising Pd-supported yttrium manganate YMnO 3 , Exhaust of Comparative Example 3 comprising Pt-supported Al 2 O 3 It is superior in the soot combustion rate than the gas purification catalyst structure. Note that the amount of Ag carried in the exhaust gas purification catalyst structure of Example 5 is the same as the amount of Pd carried by the exhaust gas purification catalyst structure of Comparative Example 2 and the Pt of the exhaust gas purification catalyst structure of Comparative Example 3. However, the exhaust gas purifying catalyst structure of Example 5 is less expensive than those of Comparative Examples 2 and 3. Therefore, it became clear that a catalyst having excellent exhaust gas purification performance and heat resistance can be obtained by combining yttrium manganate YMnO 3 and Ag.
Claims (5)
The exhaust gas purifying catalyst component according to claim 3, wherein the catalyst support is DPF.
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US9511355B2 (en) | 2013-11-26 | 2016-12-06 | Clean Diesel Technologies, Inc. (Cdti) | System and methods for using synergized PGM as a three-way catalyst |
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JP2015100758A (en) * | 2013-11-26 | 2015-06-04 | 三菱重工業株式会社 | Exhaust gas treatment system |
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