JP2001113172A - Exhaust gas purification catalyst - Google Patents
Exhaust gas purification catalystInfo
- Publication number
- JP2001113172A JP2001113172A JP29380399A JP29380399A JP2001113172A JP 2001113172 A JP2001113172 A JP 2001113172A JP 29380399 A JP29380399 A JP 29380399A JP 29380399 A JP29380399 A JP 29380399A JP 2001113172 A JP2001113172 A JP 2001113172A
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- JP
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- Prior art keywords
- layer
- catalyst
- storage
- barrier layer
- exhaust gas
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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)
-
- 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
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- B01J23/656—Manganese, technetium or rhenium
- B01J23/6562—Manganese
-
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- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/70—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
- B01J23/89—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
- B01J23/8933—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/8946—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with alkali or alkaline earth metals
-
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- 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
- B01J37/024—Multiple impregnation or coating
- B01J37/0244—Coatings comprising several layers
-
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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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
- B01J37/024—Multiple impregnation or coating
- B01J37/0246—Coatings comprising a zeolite
-
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- B01D2255/1021—Platinum
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- B01D—SEPARATION
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- B01D2255/202—Alkali metals
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- B01D2255/2042—Barium
-
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- B01D2255/2065—Cerium
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- B01D2255/20746—Cobalt
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- B01D2255/00—Catalysts
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- B01D2255/91—NOx-storage component incorporated in the catalyst
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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
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Abstract
(57)【要約】
【課題】 NOX 吸蔵還元型の排気ガス浄化用触媒の硫
黄被毒を抑制する。
【解決手段】 アルカリもしくはアルカリ土類金属を含
むNOX 吸蔵型触媒層を備えた排気ガス浄化用触媒にお
いて、NOX 吸蔵型触媒層の表層に、SOX のNOX 吸
蔵型触媒層への拡散を抑制する無機酸化物に貴金属及び
遷移金属が担持された層であるバリヤ層を設ける。好ま
しくは、前記バリヤ層の上層に、貴金属が担持されたゼ
オライト層であるSOX 吸放出材層をさらに設ける。
(57) Abstract: the NO X storage reduction type suppresses sulfur poisoning of the exhaust gas purifying catalyst. In the exhaust gas purifying catalyst having a the NO X storage catalyst layer comprising A an alkali or alkaline earth metal, on the surface layer of the NO X storage catalyst layer, diffusion into the NO X storage catalyst layer of SO X A barrier layer, which is a layer in which a noble metal and a transition metal are supported on an inorganic oxide that suppresses the occurrence of a noble metal. Preferably, the upper layer of the barrier layer, a noble metal is further provided with a SO X absorption and release material layer is a zeolite layer supported.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、自動車などの内燃
機関から排出される排気ガスを浄化するための排気ガス
浄化触媒に関し、詳しくは、リーンバーンエンジンから
の排気ガスを浄化するのに適する改良されたNOX 吸蔵
還元型の排気ガス浄化触媒に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying catalyst for purifying exhaust gas discharged from an internal combustion engine of an automobile or the like, and more particularly, to an improvement suitable for purifying exhaust gas from a lean burn engine. It relates the NO X storage-reduction type exhaust gas purifying catalyst that is.
【0002】[0002]
【従来の技術】近年、地球保護の観点より、自動車等の
内燃機関から排出される二酸化炭素(CO2 )の総量を
抑えることが世界的な課題となり、排気ガス規制及び燃
費規制が年々強化されつつある。この対応策として、燃
費向上の目的でリーンバーンエンジンが開発され、その
排気ガスを浄化する目的で、従来の三元触媒にリーン雰
囲気でNOX を吸蔵する機能を付加させたNOX 吸蔵還
元型三元触媒が開発され、上記課題に対して一定の成功
を収めている。2. Description of the Related Art In recent years, from the viewpoint of protecting the earth, it has become a worldwide problem to reduce the total amount of carbon dioxide (CO 2 ) emitted from internal combustion engines of automobiles and the like, and regulations on exhaust gas and fuel consumption have been strengthened year by year. It is getting. As a countermeasure, a lean-burn engine has been developed for the purpose of improving fuel economy, the purpose of purifying the exhaust gas, NO X storage reduction obtained by adding a function of occluding NO X in a lean atmosphere to a conventional three-way catalyst Three-way catalysts have been developed and have achieved some success with the above issues.
【0003】このリーンバーンエンジンは、燃料を、常
時は空燃比(A/F)がリーン(空気過剰)の条件下で
燃焼させ、一時的にストイキ(理論空燃比)〜リッチ
(燃料過剰)の条件下で燃焼させる。排気ガス中のHC
やCOは、リーン側で酸化性雰囲気と触媒の作用により
効率的に燃焼除去され、一方、NOX はリーン側では吸
蔵材に捕捉され、それが一時的なストイキ〜リッチ条件
下において放出され、その一時的還元性雰囲気と触媒の
作用により還元浄化される。これらの空燃比制御とNO
X 吸蔵型三元触媒の作用により、全体として、燃費を向
上させると同時に排気ガス中のHC、CO、NOX を効
率よく浄化することができる。[0003] In this lean burn engine, fuel is normally burned under the condition that the air-fuel ratio (A / F) is lean (excess air), and the fuel is temporarily stoichiometric (stoichiometric air-fuel ratio) to rich (excess fuel). Burn under conditions. HC in exhaust gas
And CO is efficiently burned and removed by the action of an oxidizing atmosphere and the catalyst in the lean side, whereas, NO X is trapped by the occluding material in the lean side, it is released in a temporary stoichiometric-rich conditions, It is reduced and purified by the action of the temporary reducing atmosphere and the catalyst. These air-fuel ratio controls and NO
By the action of X storage type three-way catalyst, as a whole, HC simultaneously exhaust gas when improving the fuel economy, CO, can be purified efficiently NO X.
【0004】[0004]
【発明が解決しようとする課題】しかしながら、燃料中
には微量ながら硫黄成分が含まれており、これが燃焼時
に酸化され、又は触媒上で酸化されてSOX が生成す
る。このSOX は酸性であり、NOX 吸蔵材は塩基性で
あることから、SOX はNOX 吸蔵材と反応して硫酸塩
を形成する。この硫酸塩は、結合が強固であるためSO
X がNOX 吸蔵材から容易に離脱せず、その結果、NO
X 吸蔵材のNOX 吸蔵能力が失われ、NOX浄化能力が
経時的に低下する。この現象はNOX 吸蔵材の硫黄被毒
として知られており、吸蔵材を使用したリーンバーンシ
ステムにおける最大の問題の一つである。However, a small amount of sulfur component is contained in the fuel, which is oxidized at the time of combustion or oxidized on a catalyst to produce SO X. Since this SO X is acidic and the NO X storage material is basic, SO X reacts with the NO X storage material to form sulfate. This sulfate has a strong bond,
X does not readily release from the NO X storage material, resulting in NO
The NO X storage ability of the X storage material is lost, and the NO X purification ability decreases over time. This phenomenon is known as the sulfur poisoning of the NO X storage component is one of the biggest problems in the lean-burn system using storage material.
【0005】このような吸蔵還元型NOX 触媒の耐硫黄
被毒性を向上させるための対応策として、特開平8−9
9034号にTiO2 、SiO2 又はZrO2 とAl2
O3を混合又は複合化した系が提案されている。このよ
うな系は、NOX 吸蔵材へのSOX の付着を抑制する効
果、及び排気ガスのA/F変動(リーン→リッチ)に伴
って付着したSOX の脱離を促進する効果が確認されて
いる。しかしながら、付着したSOX の脱離を効率的に
行うためには、通常の運転状態を上回る高温を要するた
め、長期間使用すると徐々にNOX 吸蔵材の被毒が進
み、NOX 浄化性能が低下するという問題がある。[0005] As countermeasures for improving the sulfur-poisoning resistance of such occlusion reduction type NO X catalyst, JP-A-8-9
No. 9034, TiO 2 , SiO 2 or ZrO 2 and Al 2
A system in which O 3 is mixed or complexed has been proposed. Such a system is confirmed to have the effect of suppressing the attachment of SO X to the NO X storage material and the effect of promoting the desorption of SO X attached to the exhaust gas due to A / F fluctuation (lean → rich). Have been. However, in order to efficiently desorb the attached SO X, a higher temperature than normal operating conditions is required. Therefore, the poisoning of the NO X storage material gradually progresses over a long period of use, and the NO X purification performance is reduced. There is a problem of lowering.
【0006】また、特開平11−156159号に、N
OX 吸蔵層に加えて、排気ガス中のSOX をリーン側で
吸収しストイキ〜リッチ側でそれを放出するセリア等の
酸化物からなる機能層を排気ガス接触側に設け、NOX
吸蔵層にSOX が到達するのを抑える触媒構造が提案さ
れている。しかしながら、かかるセリア層は、SOX を
捕捉・放出する性能が不足するため、一部のSOX がN
OX 吸蔵層まで到達し、下層のNOX 吸蔵層の浄化性能
が短期間に著しく低下するという問題がある。[0006] Japanese Patent Application Laid-Open No. H11-156159 discloses N
In addition to O X occlusion layer is provided with a functional layer comprising an oxide of ceria or the like for releasing it to SO X in the exhaust gas is absorbed in the lean side stoichiometric-rich side to the exhaust gas contacting side, NO X
A catalyst structure for suppressing SO X from reaching the storage layer has been proposed. However, such a ceria layer lacks the ability to capture and release SO x , so that some of the SO x
Reach O X occlusion layer, there is a problem that the purification performance of the underlying the NO X storage layer is significantly reduced in a short period of time.
【0007】従って、本発明は、SOX を強固に捕捉す
るバリヤ層を設けることでSOX がNOX 吸蔵層に到達
することを抑え、NOX 吸蔵層の性能を最大限に維持さ
せる改良されたNOX 吸蔵還元型排気ガス浄化触媒を提
供することを目的とする。Accordingly, the present invention suppresses the SO X reaches the NO X storage layer by providing a barrier layer which firmly capture the SO X, improved to maintain maximum performance of the NO X storage layer and to provide a the NO X storage-reduction type exhaust gas purifying catalyst.
【0008】[0008]
【課題を解決するための手段】上記課題を解決するた
め、担体上に浄化触媒金属と共にNOX 吸蔵材としてア
ルカリもしくはアルカリ土類金属を含むNOX 吸蔵型触
媒層を有し、前記NOX吸蔵型触媒層の表面に、SOX
のNOX 吸蔵材への拡散を抑制するバリヤ層を備え、前
記バリヤ層が貴金属及び遷移金属が担持された無機酸化
物からなる層であることを特徴とする排気ガス浄化触媒
が提供される。In order to solve the above problems SUMMARY OF THE INVENTION have the NO X storage catalyst layer containing an alkali or alkaline earth metal as the NO X storage material with purifying catalyst metal on a support, wherein the NO X storage SO X
An exhaust gas purifying catalyst, comprising a barrier layer that suppresses the diffusion of NOx into the NO X storage material, wherein the barrier layer is a layer made of an inorganic oxide carrying a noble metal and a transition metal.
【0009】本発明で特定するバリヤ層は、無機酸化物
に貴金属と遷移金属の双方が担持された層である。この
バリヤ層に含まれる貴金属は、リーン側でSOX を酸化
し、その酸化されたSOX を遷移金属が強固に捕捉する
ことにより、SOX がNOX吸蔵材に到達することを阻
止する作用をする。また、バリヤ層の貴金属はストイキ
〜リッチ側でこの酸化されたSOX を還元する作用を行
い、ストイキ〜リッチ側で遷移金属との結合が切れ、S
OX はバリヤ層から放出される。The barrier layer specified in the present invention is a layer in which both a noble metal and a transition metal are supported on an inorganic oxide. The noble metal contained in the barrier layer oxidizes SO X on the lean side, and the transition metal firmly captures the oxidized SO X , thereby preventing SO X from reaching the NO X storage material. do. Further, the noble metal of the barrier layer acts to reduce the oxidized SO X on the stoichiometric to rich side, and breaks the bond with the transition metal on the stoichiometric to rich side.
O X is released from the barrier layer.
【0010】遷移金属は、リーン側で酸化されたSOX
を強固に捕捉するけれどもストイキ〜リッチ側ではSO
X を放出することが可能であり、従って、バリヤ層のS
OX吸収能力は飽和することなく、NOX 吸蔵型触媒層
へのSOX の到達を安定して抑制することができる。The transition metal is SO X oxidized on the lean side.
, But on the rich side, SO
X can be released, and thus the S
The O X absorption capacity does not saturate, and the arrival of SO X to the NO X storage type catalyst layer can be suppressed stably.
【0011】本発明の好ましい態様において、前記バリ
ヤ層の上層にSOX 吸放出材層をさらに備える。好まし
くは、SOX 吸放出材層は、貴金属が担持されたゼオラ
イト層である。このSOX 吸放出材層は、貴金属が、リ
ーン側でSOX を酸化し、それをゼオライト等が捕捉
し、かつストイキ〜リッチ側でこの酸化されたSOX を
還元し、ゼオライト等との結合が切れ、SOX がSOX
吸放出材層から放出される。In a preferred embodiment of the present invention, further comprising a SO X absorption and release material layer on the upper layer of the barrier layer. Preferably, the SO X absorbent material layer is a zeolite layer carrying a noble metal. In the SO X absorbing / releasing material layer, the noble metal oxidizes SO X on the lean side, captures it by zeolite and the like, and reduces this oxidized SO X on the stoichiometric side to the rich side to bind with zeolite and the like. Has run out and SO X becomes SO X
It is released from the material layer.
【0012】SOX 吸放出材層は、バリヤ層よりも広範
囲な条件、とりわけ広い温度範囲でSOX を捕捉するこ
とができるものであり、SOX は先ずSOX 吸放出材層
で捕捉される。しかし、SOX 吸放出材層はバリヤ層よ
りもSOX を捕捉する力が弱いため、SOX がSOX 吸
放出材層を通り抜けることがある。このようにSOX吸
放出材層を通り抜けたSOX を強い結合力で捕捉する。
こうして、バリヤ層の上にSOX 吸放出材層を設けるこ
とによって、SOX のNOX 吸蔵材への到達をより完全
に抑制することができる。The SO X absorber layer can capture SO X over a wider range of conditions than the barrier layer, especially over a wider temperature range. SO X is first captured by the SO X absorber layer. . However, since the SO X absorbing / releasing material layer has a weaker ability to capture SO X than the barrier layer, SO X may pass through the SO X absorbing / releasing material layer. Thus capture a strong bonding force to SO X passing through the SO X absorbing and releasing material layer.
Thus, by providing the SO X absorbing and releasing material layer over the barrier layer, it can be more completely suppressed from reaching the the NO X storage material SO X.
【0013】[0013]
【発明の実施の形態】図1は、本発明の排気ガス浄化用
触媒の部分拡大断面図である。この排気ガス浄化用触媒
1は、担体基材2とその担体基材表面に被覆されたNO
X 吸蔵型触媒層3から構成されている。担体基材として
は、コーデェライト等の耐熱セラミックからなるモノリ
ス担体基材が好ましい。FIG. 1 is a partially enlarged sectional view of an exhaust gas purifying catalyst according to the present invention. The exhaust gas purifying catalyst 1 is composed of a carrier substrate 2 and a NO.
It is composed of an X storage catalyst layer 3. As the carrier substrate, a monolith carrier substrate made of a heat-resistant ceramic such as cordierite is preferable.
【0014】担体基材2は、NOX 吸蔵型触媒層3で被
覆される。このNOX 吸蔵型触媒層は、浄化触媒金属と
共にNOX 吸蔵材としてアルカリもしくは/およびアル
カリ土類金属を含んでなるもので、好ましくは、アルミ
ナ、シリカ、ジルコニア、シリカ−アルミナ、ゼオライ
ト等の無機酸化物多孔質体に担持された貴金属とアルカ
リもしくはアルカリ土類金属からなる層である。The carrier substrate 2 is covered with a NO x storage type catalyst layer 3. This NO X storage type catalyst layer contains an alkali or / and alkaline earth metal as a NO X storage material together with a purification catalyst metal, and is preferably an inorganic material such as alumina, silica, zirconia, silica-alumina, or zeolite. This is a layer composed of a noble metal and an alkali or alkaline earth metal supported on an oxide porous body.
【0015】この浄化触媒金属は、リーン側で、NOX
をアルカリ金属等で捕捉され易いNO3 - の形まで酸化
させ、ストイキ〜リッチ側でそれを還元する作用をす
る。その担持量は、NOX 吸蔵型触媒層3の重量あたり
0.5〜5wt%が好ましく、浄化触媒金属には、白金、
金、ルテニウム、ロジウム、パラジウムが例示される。[0015] The purification catalyst metal is in the lean side, NO X
Is oxidized to the form of NO 3 − which is easily captured by an alkali metal or the like, and acts to reduce it on the stoichiometric to rich side. The supported amount is preferably 0.5 to 5 wt% per weight of the NO X storage type catalyst layer 3, and the purification catalyst metal includes platinum,
Examples include gold, ruthenium, rhodium and palladium.
【0016】NOX 吸蔵型触媒層には、NOX 吸蔵材と
してのアルカリもしくはアルカリ土類金属が含まれる。
この吸蔵材は、リーン側でNOX を捕捉し、ストイキ〜
リッチ側でそれを放出する作用をする。アルカリ金属と
しては、リチウム、ナトリウム、カリウム、ルビジウ
ム、セシウム、フランシウムが例示される。アルカリ土
類金属としては、ベリリウム、マグネシウム、カルシウ
ム、ストロンチウム、バリウムが例示される。アルカリ
もしくはアルカリ土類金属の担持量は、担体基材の1リ
ットルあたり0.05〜0.5モルが好ましい。The NO X storage catalyst layer contains an alkali or alkaline earth metal as a NO X storage material.
The absorbing material captures NO X in the lean side, stoichiometric ~
It acts to release it on the rich side. Examples of the alkali metal include lithium, sodium, potassium, rubidium, cesium, and francium. Examples of the alkaline earth metal include beryllium, magnesium, calcium, strontium, and barium. The supporting amount of the alkali or alkaline earth metal is preferably 0.05 to 0.5 mol per liter of the carrier substrate.
【0017】このNOX 吸蔵型触媒層3の表層は、バリ
ヤ層4で被覆される。このバリヤ層は、無機酸化物に貴
金属及び遷移金属が担持された層である。無機酸化物に
は、アルミナ、シリカ、ジルコニア、シリカ−アルミ
ナ、ゼオライト等が用いられ、好ましくは、活性アルミ
ナである。貴金属には、白金、金、ルテニウム、ロジウ
ム、パラジウムが例示され、好ましくは白金である。遷
移金属は、周期律表の3A〜7A族、8族、及び1B族
の元素であり、チタン、バナジウム、クロム、マンガ
ン、鉄、コバルト、ニッケル、銅、ジルコニウム、ニオ
ブ、ランタン、セリウムが例示され、好ましくは、硫酸
塩の分解し易さから、マンガン、鉄、コバルト、ニッケ
ル、銅である。The surface layer of the NO x storage type catalyst layer 3 is covered with a barrier layer 4. This barrier layer is a layer in which a noble metal and a transition metal are supported on an inorganic oxide. As the inorganic oxide, alumina, silica, zirconia, silica-alumina, zeolite and the like are used, and activated alumina is preferable. Examples of the noble metal include platinum, gold, ruthenium, rhodium and palladium, and preferably platinum. Transition metals are elements of groups 3A to 7A, 8 and 1B of the periodic table, and include titanium, vanadium, chromium, manganese, iron, cobalt, nickel, copper, zirconium, niobium, lanthanum, and cerium. Preferably, manganese, iron, cobalt, nickel, and copper are used because of easy decomposition of sulfate.
【0018】このバリヤ層4は、バリヤ層の重量あたり
少なくとも0.3wt%の貴金属を含み、好ましくは0.
5〜5wt%の貴金属を含む。また、遷移金属の量は、バ
リヤ層の重量あたり少なくとも0.3×10-3モル/
g、好ましくは0.5×10-3〜1.0×10-3モル/
gである。また、バリヤ層の厚さは、少なくとも3μm
であり、好ましくは10〜20μmである。The barrier layer 4 contains at least 0.3% by weight of a noble metal per weight of the barrier layer, and preferably contains noble metal.
Contains 5-5 wt% precious metal. Also, the amount of transition metal is at least 0.3 × 10 −3 mol / weight per barrier layer weight.
g, preferably 0.5 × 10 −3 to 1.0 × 10 −3 mol /
g. The thickness of the barrier layer is at least 3 μm.
And preferably 10 to 20 μm.
【0019】本発明における好ましい態様において、バ
リヤ層の上にさらにSOX 吸放出材層5を設ける。この
SOX 吸放出材層は、好ましくは、モルデナイト等のゼ
オライトの上に白金等の貴金属が担持された層である。
貴金属の量は、バリヤ層の重量あたり少なくとも0.3
wt%、好ましくは0.5〜5wt%であり、バリヤ層の厚
さは少なくとも3μmであり、好ましくは10〜20μ
mである。In a preferred embodiment of the present invention, further provided with a SO X absorbing material layer 5 on the barrier layer. This SO X absorbing / releasing material layer is preferably a layer in which a noble metal such as platinum is supported on a zeolite such as mordenite.
The amount of noble metal should be at least 0.3 per weight of barrier layer
wt%, preferably 0.5-5 wt%, and the thickness of the barrier layer is at least 3 μm, preferably 10-20 μm.
m.
【0020】本発明の排気ガス浄化触媒は、NOX 吸蔵
型触媒層とバリヤ層を備え、好ましい態様としてSOX
吸放出材層をさらに備えるが、これらの層は次のような
機能をするものと考えられる。The exhaust gas purifying catalyst of the present invention includes a the NO X storage catalyst layer and the barrier layer, SO a preferred embodiment X
It further comprises layers of absorbent material, which are believed to perform the following functions.
【0021】NOX 吸蔵材は、リーン条件下で含まれる
浄化触媒金属によってNOX をNO 3 - の形まで酸化さ
せ、アルカリ金属等の作用によってこれを捕捉する。こ
のように、NOX 吸蔵材は、リーン条件下でNOX を吸
収するが、排気ガス中には微量ながらSOX が含まれて
おり、例えばSO2 は、貴金属の表面上で酸化されてS
O3 となり、さらに雰囲気下で酸化されてSO4 - の形
で吸蔵層を拡散しながら、硫酸塩を生成する。この硫酸
塩は硝酸塩より分解し難く、ストイキ〜リッチ条件下に
おいても分解されずにそのまま残り、従って、吸蔵材層
には経時的に硫酸塩が増大し、吸蔵材で捕捉し得るNO
X 量が低下することになる。NOXOccupants are included under lean conditions
NO by purification catalyst metalXNO Three -Oxidized to the shape of
And capture it by the action of an alkali metal or the like. This
Like, NOXThe storage material is NO under lean conditions.XSuck
But a small amount of SO in the exhaust gasXIncludes
Yes, for example SOTwoIs oxidized on the surface of the noble metal to form S
OThreeAnd further oxidized in an atmosphere to form SOFour -Form of
To generate sulfate while diffusing the occlusion layer. This sulfuric acid
Salt is harder to decompose than nitrate, under stoichiometric to rich conditions
Remains without being decomposed, and therefore, the occlusion material layer
The sulfate increases with time, and NO that can be captured by the storage material
XThe amount will be reduced.
【0022】バリヤ層は、かかるNOX 吸蔵材の性能低
下を抑えるものであり、バリヤ層に含まれる貴金属と遷
移金属の作用により、NOX 吸蔵型触媒層の手前でSO
X を強固に捕捉することにより、NOX 吸蔵材の硫黄被
毒を防止するものである。即ち、バリヤ層は、NOX 吸
蔵型触媒層に対して、SOX が到達することを防ぐSO
X 遮蔽作用を提供するが、これは、リーン条件下で、貴
金属がSOX をSO3 に酸化し、それが酸化性雰囲気下
でSO4 - の形に変わり、バリヤ層に存在する遷移金属
がそのSO4 - を強く捕捉するためである。一方、スト
イキ〜リッチ条件下では、貴金属がSO4 - の排気ガス
中のHCやCOとの還元反応を促進し、再びSO4 - が
SOX の形態となって排気ガス中に放出される。The barrier layer suppresses the deterioration of the performance of the NO X storage material, and the action of the noble metal and the transition metal contained in the barrier layer causes the SO x to be in front of the NO X storage catalyst layer.
By firmly capture the X, thereby preventing sulfur poisoning of the NO X occluding material. That is, the barrier layer prevents SO X from reaching the NO X storage catalyst layer.
To provide an X-shielding effect, which is under lean conditions, precious metal oxidizes SO X into SO 3, it SO 4 in an oxidizing atmosphere - changes to a, transition metal present in the barrier layer its SO 4 - in order to capture strong. On the other hand, the stoichiometric-rich conditions, precious metal SO 4 - promoting the reduction reaction with HC and CO in the exhaust gas again SO 4 - are released into the exhaust gas becomes the form of SO X.
【0023】言い換えると、遷移金属はSO4 - と強固
に結合することができる一方、その結合は、NOX 吸蔵
型触媒層のNOX 吸蔵材とSO4 - との結合とは異な
り、貴金属の存在下の還元雰囲気の中では切れることが
でき、SOX が排気ガス中に放出されため、バリヤ層の
SOX 捕捉性能は飽和することはない。従って、バリヤ
層は、NOX 吸蔵型触媒層に対して、経時的に安定して
SOX 遮蔽作用を提供することができるのである。[0023] In other words, the transition metal SO 4 - one which can be firmly coupled with, the binding, the NO X storage-type catalytic layer the NO X storage material and SO 4 - Unlike binding to, noble metals Since it can be cut off in the presence of a reducing atmosphere and SO X is released into the exhaust gas, the SO X trapping performance of the barrier layer does not saturate. Therefore, the barrier layer can provide an SO X shielding effect stably with time to the NO X storage type catalyst layer.
【0024】また、NOX に関して、バリヤ層に含まれ
る貴金属の作用でNOX の少なくとも一部はNO3 - の
形まで酸化されるが、遷移金属はそれを強固に捕捉する
結合力を有しない。従って、バリヤ層は、NOX に対し
てSOX を優先的に捕捉することにより、NOX 吸蔵材
に対するバリヤ層として作用するのである。Further, with respect to NO X, at least a portion of the NO X by the action of the noble metal contained in the barrier layer NO 3 - no binding force but is oxidized to a form of the transition metal to catch it firmly . Accordingly, the barrier layer, by capturing SO X preferentially relative to NO X, is to act as a barrier layer against the NO X storage material.
【0025】このようにして、SOX はNOX 吸蔵型触
媒層の上層のバリヤ層で吸着・離脱を繰り返し、SOX
の捕捉効率が飽和することなく、NOX 吸蔵材への拡散
が抑制されるため、NOX 吸蔵型触媒層の被毒を経時的
に安定して抑えることが可能となる。As described above, SO X is repeatedly adsorbed and desorbed by the upper barrier layer of the NO X storage type catalyst layer, and SO X
Capture efficiency without saturating, the diffusion into the NO X storage material is suppressed, it is possible to suppress stable over time poisoning of the NO X storage catalyst layer.
【0026】本発明における好ましい態様において、バ
リヤ層の上にさらにSOX 吸放出材層5を設ける。この
SOX 吸放出材層では、リッチ条件下でSOX 吸放出材
層に含まれる貴金属がSOX をSO3 に酸化し、それが
酸化性の雰囲気下でSO4 -の形に変わるため、それを
ゼオライトが捕捉することでSOX がバリヤ層に到達す
ることを防ぐ。一方、ストイキ〜リッチ条件下では、貴
金属の触媒作用によってSO4 - を排気ガス中のHCや
COと反応を促進させて再びSOX の形態で排気ガス中
に放出することができる。In a preferred embodiment of the present invention, further provided with a SO X absorbing material layer 5 on the barrier layer. This SO X absorbing and releasing material layer, a noble metal contained in the SO X absorbing and releasing material layer under rich conditions oxidizes SO X into SO 3, it SO 4 under an atmosphere of an oxidizing - for changes to a, The capture of this by the zeolite prevents SO X from reaching the barrier layer. On the other hand, the stoichiometric-rich conditions, SO 4 by the catalytic action of the noble metal - may be released into the exhaust gas in the form of HC and CO again SO X by promoting the reaction in the exhaust gas.
【0027】ここで、このSOX 吸放出材層は、主とし
て遷移金属とゼオライト等との成分の相違により、バリ
ヤ層よりもSOX の捕捉力が弱く、従って、バリヤ層よ
りもSOX 捕捉効率が低いが、バリヤ層よりも広い温度
範囲でSOX を捕捉できる。このSOX 吸放出材層をバ
リヤ層の排気ガス側に設けることで、バリヤ層のSO X
捕捉の負担が軽減されると同時にSOX の捕捉が可能な
温度範囲が広がり、全体としてSOX 捕捉効率をより高
くすることができる。Here, this SOXThe material layer is mainly
Due to differences in components between the transition metal and zeolite, etc.
SO layer than layerXOf the barrier layer, and therefore the barrier layer
RIMO SOXLow trapping efficiency but wider temperature than barrier layer
SO in rangeXCan be captured. This SOXAbsorbing material layer
By providing it on the exhaust gas side of the rear layer, the SOI of the barrier layer can be reduced. X
At the same time as the burden of capturing is reduced, SOXCan be captured
The temperature range expands and SOXHigher capture efficiency
Can be done.
【0028】加えて、バリヤ層とSOX 吸放出材層の双
方が貴金属を含んでいることから、排気ガス中のNOX
がバリヤ層とSOX 吸放出材層の双方を通ってNOX 吸
蔵型触媒層に到達するときは、NOX は高い割合で捕捉
され易いNO3 - の形まで酸化されており、従って、N
OX 吸蔵効率も高くなる。In addition, since both the barrier layer and the SO x absorbing / releasing material layer contain a noble metal, NO x in the exhaust gas
When but to reach the NO X storage catalyst layer through both the barrier layer and the SO X absorbing and releasing material layer, NO X is captured easily NO 3 at a high rate - are oxidized to form, and therefore, N
O X storage efficiency is also increased.
【0029】なお、本発明者らにより、前述した先行技
術のセリア等の酸化物からなり貴金属を含まない層を備
えた触媒構成においては、SOX を捕捉する効率が低
く、かかる層がSOX を飽和した後は有意なSOX 吸放
出効果が見られないことが確認されている。これは、セ
リア単独ではSOX をSO3 にする触媒作用が低いこと
から、SOX が捕捉され易いSO4 - に転化されず、ま
た、セリア単独では、一部に転化されて捕捉されたSO
4 - のSOX への還元作用も低いことから、SO X を放
出する効率も劣るためと考えられる。It should be noted that the present inventors described the prior art described above.
It is equipped with a layer made of oxide such as ceria, which does not contain precious metals.
In the obtained catalyst configuration, SOXLow capture efficiency
And the layer is SOXSignificant SO after saturationXAbsorption and release
No effect has been confirmed. This is
SO for rear aloneXTo SOThreeLow catalysis
From SOXSO that is easily capturedFour -Is not converted to
In addition, in the case of ceria alone, the SO
Four -SOXHas a low reducing effect on XRelease
It is considered that the efficiency of the emission is low.
【0030】[0030]
【実施例】実施例1 直径30mm×長さ50mmの円筒状モノリス担体に、
活性Al2 O3 からなるウォッシュコート層を形成し、
Ptジニトロジアミン水溶液に浸した後乾燥させること
で、触媒容積1リットルあたり2gのPtを担持した。
次に酢酸バリウム水溶液を用いて、触媒容積1リットル
あたり0.2モルのBaを担持し、500℃で1時間焼
成した。次に別途、イオン交換水とバインダー、予めP
tとCoとが担持された活性Al2 O3 粉末、及び安定
剤を含むスラリーを調製し、上記モノリス触媒上にウォ
ッシュコートを行った後、乾燥・焼成してSOX バリヤ
層を形成した。このとき、SOX バリヤ層の活性アルミ
ナ180gあたりのCo担持量は0.1モル(3.3wt
%)、Ptは2wt%であり、コート量は約30gであっ
た。EXAMPLES Example 1 A cylindrical monolithic carrier having a diameter of 30 mm and a length of 50 mm was used.
Forming a washcoat layer of active Al 2 O 3 ,
By immersing in an aqueous solution of Pt dinitrodiamine and then drying, 2 g of Pt was supported per liter of catalyst volume.
Next, using an aqueous barium acetate solution, 0.2 mol of Ba was supported per liter of catalyst volume, and calcined at 500 ° C. for 1 hour. Next, separately, ion-exchanged water and binder, P
A slurry containing an active Al 2 O 3 powder carrying t and Co and a stabilizer was prepared, wash-coated on the monolith catalyst, dried and fired to form a SO X barrier layer. At this time, the amount of supported Co per 180 g of activated alumina in the SO X barrier layer was 0.1 mol (3.3 wt.
%), Pt was 2 wt%, and the coating amount was about 30 g.
【0031】実施例2 実施例1と同様な操作で、モノリス担体上にPtとBa
が担持されたNOX 吸蔵型触媒層を形成し、その表面に
Pt、Mn、及びAl2 O3 からなるバリヤ層を形成し
た。このとき、NOX 吸蔵型触媒層には触媒容積1リッ
トルあたり2gのPtと0.2モルのBaが担持され、
バリヤ層は2wt%のPt、0.1モルのMnを含み、コ
ート量は約30gであった。Example 2 In the same manner as in Example 1, Pt and Ba were placed on a monolithic carrier.
Was formed, and a barrier layer composed of Pt, Mn, and Al 2 O 3 was formed on the surface of the NO X storage catalyst layer. At this time, 2 g of Pt and 0.2 mol of Ba were supported per liter of catalyst volume on the NO x storage catalyst layer,
The barrier layer contained 2 wt% Pt, 0.1 mol Mn, and the coating amount was about 30 g.
【0032】実施例3 実施例1と同様な操作で、触媒容積1リットルあたり2
gのPtと0.2モルのBaが担持されたNOX 吸蔵型
触媒層を形成し、その表面に触媒容積1リットルあたり
0.1モルのFeと2wt%のPt、及びAl2 O3 から
なるバリヤ層を形成した。バリヤ層のコート量は、触媒
容積1リットルあたり約30gであった。Example 3 The same operation as in Example 1 was repeated except that the catalyst volume was 2
g of Pt and 0.2 mol of Ba were formed on the NO x storage catalyst layer, and the surface thereof was formed from 0.1 mol of Fe, 2 wt% of Pt, and Al 2 O 3 per liter of catalyst volume. A barrier layer was formed. The coating amount of the barrier layer was about 30 g per liter of catalyst volume.
【0033】実施例4 実施例1と同様な操作で、モノリス担体上にPtとBa
が担持されたNOX 吸蔵型触媒層を形成し、その表面に
Pt、Ni、及びAl2 O3 からなるバリヤ層を形成し
た。このとき、NOX 吸蔵型触媒層には触媒容積1リッ
トルあたり2gのPtと0.2モルのBaが担持され、
バリヤ層は2wt%のPt、0.1モルのNiを含み、コ
ート量は約30gであった。Example 4 In the same manner as in Example 1, Pt and Ba were placed on a monolithic carrier.
Was formed, and a barrier layer composed of Pt, Ni, and Al 2 O 3 was formed on the surface of the NO x storage catalyst layer. At this time, 2 g of Pt and 0.2 mol of Ba were supported per liter of catalyst volume on the NO x storage catalyst layer,
The barrier layer contained 2 wt% Pt, 0.1 mol Ni, and the coating amount was about 30 g.
【0034】実施例5 実施例1と同様な操作で、モノリス担体上にPtとBa
が担持されたNOX 吸蔵型触媒層を形成し、その表面に
Pt、Cu、及びAl2 O3 からなるバリヤ層を形成し
た。このとき、NOX 吸蔵型触媒層には触媒容積1リッ
トルあたり2gのPtと0.2モルのBaが担持され、
バリヤ層は2wt%のPt、0.1モルのCuを含み、コ
ート量は約30gであった。Example 5 In the same manner as in Example 1, Pt and Ba were placed on a monolithic carrier.
Was formed, and a barrier layer made of Pt, Cu, and Al 2 O 3 was formed on the surface of the NO x storage catalyst layer. At this time, 2 g of Pt and 0.2 mol of Ba were supported per liter of catalyst volume on the NO x storage catalyst layer,
The barrier layer contained 2 wt% Pt, 0.1 mol Cu, and the coating amount was about 30 g.
【0035】実施例6 実施例1と同様な操作で、モノリス担体上にPtとBa
が担持されたNOX 吸蔵型触媒層を形成し、その表面に
Pt、Zn、及びAl2 O3 からなるバリヤ層を形成し
た。このとき、NOX 吸蔵型触媒層には触媒容積1リッ
トルあたり2gのPtと0.2モルのBaが担持され、
バリヤ層は2wt%のPt、0.1モルのZnを含み、コ
ート量は約30gであった。Example 6 In the same manner as in Example 1, Pt and Ba were placed on a monolithic carrier.
Was formed, and a barrier layer composed of Pt, Zn, and Al 2 O 3 was formed on the surface of the NO x storage catalyst layer. At this time, 2 g of Pt and 0.2 mol of Ba were supported per liter of catalyst volume on the NO x storage catalyst layer,
The barrier layer contained 2 wt% Pt and 0.1 mol Zn, and the coating amount was about 30 g.
【0036】実施例7 実施例1と同様な操作で、モノリス担体上にPtとBa
が担持されたNOX 吸蔵型触媒層を形成し、その表面に
Pt、Ce、及びAl2 O3 からなるバリヤ層を形成し
た。このとき、NOX 吸蔵型触媒層には触媒容積1リッ
トルあたり2gのPtと0.2モルのBaが担持され、
バリヤ層は2wt%のPt、0.1モルのCeを含み、コ
ート量は約30gであった。Example 7 In the same manner as in Example 1, Pt and Ba were placed on a monolithic carrier.
Was formed, and a barrier layer composed of Pt, Ce, and Al 2 O 3 was formed on the surface of the NO x storage catalyst layer. At this time, 2 g of Pt and 0.2 mol of Ba were supported per liter of catalyst volume on the NO x storage catalyst layer,
The barrier layer contained 2 wt% Pt, 0.1 mole Ce, and the coating amount was about 30 g.
【0037】実施例8 実施例1と同様な操作で、モノリス担体上にPtとBa
が担持されたNOX 吸蔵型触媒層を形成し、その表面に
Pt、Co、及びAl2 O3 からなるバリヤ層を形成し
た。このとき、NOX 吸蔵型触媒層には触媒容積1リッ
トルあたり2gのPtと0.2モルのBaが担持され、
バリヤ層は2wt%のPt、0.1モルのCoを含み、コ
ート量は約30gであった。Example 8 In the same manner as in Example 1, Pt and Ba were placed on a monolithic carrier.
Was formed, and a barrier layer composed of Pt, Co, and Al 2 O 3 was formed on the surface of the NO X storage catalyst layer. At this time, 2 g of Pt and 0.2 mol of Ba were supported per liter of catalyst volume on the NO x storage catalyst layer,
The barrier layer contained 2 wt% of Pt and 0.1 mol of Co, and the coating amount was about 30 g.
【0038】次に、予め2wt%のPtが担持されたモル
デナイト粉末、イオン交換水、バインダー、及び安定剤
を含むスラリーを調製し、このスラリーをウォッシュコ
ートしてバリヤ層上に第3層のSOX 吸放出材層を形成
した。Pt/Mor(白金が担持されたモルデナイト)
層のコート量は、触媒容積1リットルあたり20gであ
り、Ptは2wt%であった。Next, a slurry containing mordenite powder preliminarily loaded with 2 wt% of Pt, ion-exchanged water, a binder, and a stabilizer is prepared, and this slurry is wash-coated to form a third layer of SO on the barrier layer. An X absorbing / releasing material layer was formed. Pt / Mor (mordenite supporting platinum)
The coating amount of the layer was 20 g per liter of catalyst volume, and Pt was 2 wt%.
【0039】比較例1 直径30mm×長さ50mmの円筒状モノリス担体に、
活性Al2 O3 からなるウォッシュコート層を形成し、
触媒容積1リットルあたり2gのPtを担持した。次に
酢酸バリウム水溶液を用いて、触媒容積1リットルあた
り0.2モルのBaを担持し、500℃で1時間焼成し
た。Comparative Example 1 A cylindrical monolithic carrier having a diameter of 30 mm and a length of 50 mm was
Forming a washcoat layer of active Al 2 O 3 ,
2 g of Pt was supported per liter of catalyst volume. Next, using an aqueous barium acetate solution, 0.2 mol of Ba was supported per liter of catalyst volume, and calcined at 500 ° C. for 1 hour.
【0040】比較例2 実施例1と同様な操作で、モノリス担体上にPtとBa
が担持されたNOX 吸蔵型触媒層を形成し、その表面に
Pt、Mg、及びAl2 O3 からなるバリヤ層を形成し
た。このとき、NOX 吸蔵型触媒層には触媒容積1リッ
トルあたり2gのPtと0.2モルのBaが担持され、
バリヤ層は2wt%のPt、0.1モルのMgを含み、コ
ート量は約30gであった。Comparative Example 2 In the same manner as in Example 1, Pt and Ba were placed on a monolithic carrier.
Was formed, and a barrier layer made of Pt, Mg, and Al 2 O 3 was formed on the surface of the NO x storage catalyst layer. At this time, 2 g of Pt and 0.2 mol of Ba were supported per liter of catalyst volume on the NO x storage catalyst layer,
The barrier layer contained 2 wt% of Pt and 0.1 mol of Mg, and the coating amount was about 30 g.
【0041】比較例3 比較例1と同様な操作で、直径30mm×長さ50mm
の円筒状モノリス担体に、活性Al2 O3 からなるウォ
ッシュコート層を形成し、触媒容積1リットルあたり2
gのPtを担持した。次に酢酸バリウム水溶液を用い
て、触媒容積1リットルあたり0.2モルのBaを担持
し、500℃で1時間焼成した。次に実施例8と同様な
操作で、このNOX 吸蔵型触媒層の表面にPt/Mor
層を形成した。Pt/Morコート量は触媒容積1リッ
トルあたり20gであり、Ptは2wt%であった。Comparative Example 3 The same operation as in Comparative Example 1 was performed, except that the diameter was 30 mm and the length was 50 mm.
Was formed on the cylindrical monolithic carrier of the formula (1), and a wash coat layer of active Al 2 O 3 was formed.
g of Pt. Next, using an aqueous barium acetate solution, 0.2 mol of Ba was supported per liter of catalyst volume, and calcined at 500 ° C. for 1 hour. Next, in the same manner as in Example 8, Pt / Mor was applied to the surface of this NO X storage catalyst layer.
A layer was formed. The coating amount of Pt / Mor was 20 g per liter of catalyst volume, and Pt was 2 wt%.
【0042】評価法 実施例1〜9、及び比較例1〜3について、第1表に示
すモデルガス中で耐硫黄被毒性を評価した。具体的に
は、触媒に入るガス温度を400℃として、30秒間の
リッチガスと60秒間のリーンガスを交互に触媒に導入
し、1時間経過した後、各触媒のNOX 吸蔵材に付着し
た硫黄分の定量分析を行った。これらの結果を第2表に
示す。Evaluation Method Examples 1 to 9 and Comparative Examples 1 to 3 were evaluated for sulfur poisoning resistance in the model gases shown in Table 1. Specifically, the gas temperature entering the catalyst was set to 400 ° C., and the rich gas for 30 seconds and the lean gas for 60 seconds were alternately introduced into the catalyst. After 1 hour, the sulfur content adhering to the NO X storage material of each catalyst was reduced. Was quantitatively analyzed. Table 2 shows the results.
【0043】[0043]
【表1】 [Table 1]
【0044】[0044]
【表2】 [Table 2]
【0045】表2から分かるように、実施例1〜5は、
モノリス基材にウォッシュコートされたAl2 O3 にN
OX 吸蔵材としてBaと浄化触媒金属としてPtを担持
し、その吸蔵層の表面にバリヤ層としてPtと遷移金属
を含むAl2 O3 をコーティングした触媒であるが、こ
れらはいずれも、バリヤ層を含まない従来構成の触媒
(比較例1)に比べ、テスト後のNOX 吸蔵材に付着し
た硫黄分が明らかに少ない結果を呈した。As can be seen from Table 2, Examples 1 to 5
Al 2 O 3 wash-coated on monolith substrate with N
O X occlusion material of Pt supported as Ba and purification catalyst metal as, is a catalyst coated with Al 2 O 3 containing Pt and a transition metal as a barrier layer on the surface of the storage layer, both of which are barrier layer In comparison with the conventional catalyst (Comparative Example 1) containing no NO, the sulfur content adhering to the NO X storage material after the test was clearly smaller.
【0046】実施例6と7は、実施例1〜5とは別の希
土類金属を含むAl2 O3 をバリヤ層としてコーティン
グした触媒であるが、あまり良好な結果は得られていな
い。これは、バリヤ層に含まれる元素の硫酸塩の分解し
易さに起因するものと考えられる。一方、バリヤ層の上
にSOX 吸放出機能の優れたモルデナイト層をさらに形
成した実施例9は、さらに良好な結果を示している。こ
れは、前述のバリヤ層とSOX 吸放出材層の二重の効果
によるものと考えられる。Examples 6 and 7 are catalysts coated with Al 2 O 3 containing a rare earth metal as a barrier layer, which are different from those of Examples 1 to 5, but have not obtained very good results. This is considered to be due to the ease of decomposition of the sulfate of the element contained in the barrier layer. On the other hand, Example 9 in which a mordenite layer having an excellent SO X absorption / desorption function was further formed on the barrier layer showed even better results. This is considered to be due to the double effect of the barrier layer and the SO X absorbing / emitting material layer.
【0047】[0047]
【発明の効果】本発明の排気ガス浄化用触媒において
は、SOX のNOX 吸蔵型触媒層への到達が抑制され、
NOX 吸蔵還元の性能低下が抑えられる。According to the exhaust gas purifying catalyst of the present invention, SO X is prevented from reaching the NO X storage catalyst layer,
A decrease in the performance of NO X storage reduction is suppressed.
【図1】本発明の排気ガス浄化用触媒の部分拡大断面図
である。FIG. 1 is a partially enlarged sectional view of an exhaust gas purifying catalyst of the present invention.
【図2】本発明の好ましい態様における排気ガス浄化用
触媒の部分拡大断面図である。FIG. 2 is a partially enlarged sectional view of an exhaust gas purifying catalyst according to a preferred embodiment of the present invention.
1…排気ガス浄化用触媒 2…担体基材 3…NOX 吸蔵型触媒層 4…バリヤ層 5…SOX 吸放出材層1 ... an exhaust gas purifying catalyst 2 ... support substrate 3 ... NO X occluding catalyst layer 4 ... barrier layer 5 ... SO X absorbing material layer
フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01J 29/22 B01J 33/00 ZABA 33/00 ZAB B01D 53/36 102B 102H Fターム(参考) 4D048 AA02 AA06 AB02 BA03X BA09X BA15X BA28X BA30X BA30Y BA31Y BA32Y BA33Y BA34Y BA35X BA35Y BA36X BA37X BA38X BB02 CC46 EA04 4G069 AA03 AA08 BA01B BA07A BA07B BB15B BC01A BC08A BC13B BC31B BC35B BC43B BC62B BC67B BC68B BC69A BC75B CA03 CA09 CA12 CA13 DA06 ED07 EE01 EE08 FA02 FB19 Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (reference) B01J 29/22 B01J 33/00 ZABA 33/00 ZAB B01D 53/36 102B 102H F-term (reference) 4D048 AA02 AA06 AB02 BA03X BA09X BA15X BA28X BA30X BA30Y BA31Y BA32Y BA33Y BA34Y BA35X BA35Y BA36X BA37X BA38X BB02 CC46 EA04 4G069 AA03 AA08 BA01B BA07A BA07B BB15B BC01A BC08A BC13B BC31B BC35B BC43B BC62B BC67BCA13 BC69BBC13B
Claims (3)
材としてアルカリもしくはアルカリ土類金属を含むNO
X 吸蔵型触媒層を有し、前記NOX 吸蔵型触媒層の表面
に、SOX のNOX 吸蔵材への拡散を抑制するバリヤ層
を備え、前記バリヤ層が貴金属及び遷移金属が担持され
た無機酸化物からなる層であることを特徴とする排気ガ
ス浄化触媒。1. A catalyst containing an alkali or alkaline earth metal as an NO X storage material together with a purification catalyst metal on a carrier.
An X storage catalyst layer, and a barrier layer for suppressing diffusion of SO X to the NO X storage material on the surface of the NO X storage catalyst layer, wherein the barrier layer carries a noble metal and a transition metal. An exhaust gas purification catalyst comprising a layer made of an inorganic oxide.
を備えた請求項1に記載の排気ガス浄化触媒。2. The exhaust gas purifying catalyst according to claim 1, further comprising an SO X absorbing / releasing material layer above the barrier layer.
されたゼオライト層である請求項2に記載の排気ガス浄
化触媒。3. The exhaust gas purifying catalyst according to claim 2, wherein the SO X absorbing / desorbing material layer is a zeolite layer carrying a noble metal.
Priority Applications (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP29380399A JP2001113172A (en) | 1999-10-15 | 1999-10-15 | Exhaust gas purification catalyst |
| FR0013018A FR2799665B1 (en) | 1999-10-15 | 2000-10-11 | CATALYST FOR THE PURIFICATION OF EXHAUST GAS |
| DE10050748A DE10050748A1 (en) | 1999-10-15 | 2000-10-13 | Exhaust gas purification catalyst |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP29380399A JP2001113172A (en) | 1999-10-15 | 1999-10-15 | Exhaust gas purification catalyst |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JP2001113172A true JP2001113172A (en) | 2001-04-24 |
Family
ID=17799362
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP29380399A Pending JP2001113172A (en) | 1999-10-15 | 1999-10-15 | Exhaust gas purification catalyst |
Country Status (3)
| Country | Link |
|---|---|
| JP (1) | JP2001113172A (en) |
| DE (1) | DE10050748A1 (en) |
| FR (1) | FR2799665B1 (en) |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002126453A (en) * | 2000-10-25 | 2002-05-08 | Toyota Motor Corp | Exhaust gas purification device |
| JP2005506900A (en) * | 2001-10-26 | 2005-03-10 | エンゲルハード・コーポレーシヨン | Layered catalyst composite |
| WO2005044426A1 (en) * | 2003-11-11 | 2005-05-19 | Valtion Teknillinen Tutkimuskeskus | Method for catalytically reducing nitrogen oxide and catalyst therefor |
| JP2006518276A (en) * | 2003-01-31 | 2006-08-10 | エンゲルハード・コーポレーシヨン | Layered catalyst composite and method of using the same |
| JP2006297350A (en) * | 2005-04-25 | 2006-11-02 | Showa Denko Kk | Photocatalyst film and manufacturing method |
| JP2006297351A (en) * | 2005-04-25 | 2006-11-02 | Showa Denko Kk | Photocatalyst film and manufacturing method |
| JP2008062235A (en) * | 2003-11-11 | 2008-03-21 | Valtion Teknillinen Tutkimuskeskus | Method for catalytically reducing nitrogen oxide and catalyst therefor |
| WO2008066197A1 (en) | 2006-12-01 | 2008-06-05 | Toyota Jidosha Kabushiki Kaisha | Exhaust gas clean-up apparatus |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP1340541A1 (en) | 2002-02-28 | 2003-09-03 | Corning Incorporated | Structured catalysts incorporating thick washcoats and method of preparation thereof |
| US6936561B2 (en) | 2002-12-02 | 2005-08-30 | Corning Incorporated | Monolithic zeolite coated structures and a method of manufacture |
| DE10328678A1 (en) * | 2003-06-26 | 2005-01-13 | Daimlerchrysler Ag | Emission control system for an internal combustion engine |
| JP4543689B2 (en) * | 2004-02-02 | 2010-09-15 | トヨタ自動車株式会社 | Exhaust purification catalyst |
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Family Cites Families (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE69503527T2 (en) * | 1994-01-20 | 1999-04-29 | Toyota Jidosha K.K., Toyota, Aichi | Catalytic converter for cleaning exhaust gases |
| JPH0857315A (en) * | 1994-08-26 | 1996-03-05 | Toyota Central Res & Dev Lab Inc | Exhaust gas purification catalyst |
| JP3368750B2 (en) * | 1996-06-14 | 2003-01-20 | 株式会社日立製作所 | Exhaust gas purification method and catalyst |
| JP3640130B2 (en) * | 1996-11-14 | 2005-04-20 | トヨタ自動車株式会社 | Exhaust gas purification catalyst and method for producing the same |
| JP3924946B2 (en) * | 1997-09-25 | 2007-06-06 | マツダ株式会社 | Exhaust gas purification material |
| JPH11276907A (en) * | 1998-03-30 | 1999-10-12 | Nissan Motor Co Ltd | Exhaust gas purification catalyst and method for producing the same |
-
1999
- 1999-10-15 JP JP29380399A patent/JP2001113172A/en active Pending
-
2000
- 2000-10-11 FR FR0013018A patent/FR2799665B1/en not_active Expired - Fee Related
- 2000-10-13 DE DE10050748A patent/DE10050748A1/en not_active Withdrawn
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002126453A (en) * | 2000-10-25 | 2002-05-08 | Toyota Motor Corp | Exhaust gas purification device |
| JP2005506900A (en) * | 2001-10-26 | 2005-03-10 | エンゲルハード・コーポレーシヨン | Layered catalyst composite |
| JP2006518276A (en) * | 2003-01-31 | 2006-08-10 | エンゲルハード・コーポレーシヨン | Layered catalyst composite and method of using the same |
| JPWO2005044426A1 (en) * | 2003-11-11 | 2007-05-17 | ヴァルティオン テクンニィルリネン ツッツキムスケスクス | Method for catalytic reduction of nitrogen oxides and catalyst therefor |
| WO2005044426A1 (en) * | 2003-11-11 | 2005-05-19 | Valtion Teknillinen Tutkimuskeskus | Method for catalytically reducing nitrogen oxide and catalyst therefor |
| JP2008062235A (en) * | 2003-11-11 | 2008-03-21 | Valtion Teknillinen Tutkimuskeskus | Method for catalytically reducing nitrogen oxide and catalyst therefor |
| US7585477B2 (en) | 2003-11-11 | 2009-09-08 | Honda Motor Co., Ltd. | Catalyst and method for catalytic reduction of nitrogen oxides |
| JP4757027B2 (en) * | 2003-11-11 | 2011-08-24 | 本田技研工業株式会社 | Catalyst for catalytic reduction of nitrogen oxides |
| JP2006297350A (en) * | 2005-04-25 | 2006-11-02 | Showa Denko Kk | Photocatalyst film and manufacturing method |
| JP2006297351A (en) * | 2005-04-25 | 2006-11-02 | Showa Denko Kk | Photocatalyst film and manufacturing method |
| WO2008066197A1 (en) | 2006-12-01 | 2008-06-05 | Toyota Jidosha Kabushiki Kaisha | Exhaust gas clean-up apparatus |
| RU2408415C1 (en) * | 2006-12-01 | 2011-01-10 | Тойота Дзидося Кабусики Кайся | Exhaust gas converter |
| US8128881B2 (en) | 2006-12-01 | 2012-03-06 | Toyota Jidosha Kabushiki Kaisha | Exhaust-gas converting apparatus |
Also Published As
| Publication number | Publication date |
|---|---|
| FR2799665B1 (en) | 2005-01-14 |
| FR2799665A1 (en) | 2001-04-20 |
| DE10050748A1 (en) | 2001-09-13 |
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