JP2002095967A - Exhaust gas cleaning catalyst - Google Patents

Exhaust gas cleaning catalyst

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Publication number
JP2002095967A
JP2002095967A JP2000290643A JP2000290643A JP2002095967A JP 2002095967 A JP2002095967 A JP 2002095967A JP 2000290643 A JP2000290643 A JP 2000290643A JP 2000290643 A JP2000290643 A JP 2000290643A JP 2002095967 A JP2002095967 A JP 2002095967A
Authority
JP
Japan
Prior art keywords
exhaust gas
sio
catalyst
substrate
alkali metal
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2000290643A
Other languages
Japanese (ja)
Inventor
Yasuaki Nakano
泰彰 仲野
Hideaki Ueno
秀章 植野
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toyota Motor Corp
Original Assignee
Toyota Motor Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toyota Motor Corp filed Critical Toyota Motor Corp
Priority to JP2000290643A priority Critical patent/JP2002095967A/en
Publication of JP2002095967A publication Critical patent/JP2002095967A/en
Pending legal-status Critical Current

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)
  • Exhaust Gas After Treatment (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide an exhaust gas cleaning catalyst, wherein a matrix is inhibited from being deteriorated so as to prevent the catalyst from deteriorating in strengths, e.g. thermal shock resistance. SOLUTION: This catalyst consists of a matrix having a composition containing SiO2 and a coat layer comprising a porous support carrying at least a noble metal and an alkali metal and formed on the surface of the matrix, wherein the matrix has an SiO2 content of 50-65 wt.% based on the entire base. Even when the SiO2 is consumed by reaction with the alkali metal, the composition of the matrix can fall within the optimal range.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は自動車エンジンから
の排気系などに用いられる排ガス浄化用触媒に関し、詳
しくは耐熱衝撃性など強度を改良した排ガス浄化用触媒
に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying catalyst used in an exhaust system of an automobile engine, and more particularly to an exhaust gas purifying catalyst having improved strength such as thermal shock resistance.

【0002】[0002]

【従来の技術】近年、二酸化炭素による地球温暖化現象
が問題となり、二酸化炭素の排出量を低減することが課
題となっている。自動車においても排ガス中の二酸化炭
素量の低減が課題となり、燃料を酸素過剰雰囲気で希薄
燃焼させるリーンバーンエンジンが開発されている。こ
のリーンバーンエンジンによれば、燃費の向上により二
酸化炭素の排出量を抑制することができる。
2. Description of the Related Art In recent years, global warming due to carbon dioxide has become a problem, and reducing carbon dioxide emissions has become an issue. In automobiles, reduction of the amount of carbon dioxide in exhaust gas has become an issue, and lean burn engines have been developed in which fuel is burned lean in an oxygen-excess atmosphere. According to this lean burn engine, the emission of carbon dioxide can be suppressed by improving fuel efficiency.

【0003】このリーンバーンエンジンにおいて、常時
は酸素過剰の燃料リーン条件で燃焼させ、間欠的に燃料
ストイキ〜リッチ条件とすることにより排ガスを還元雰
囲気としてNOx を還元浄化するシステムが開発され、実
用化されている。そしてこのシステムに最適な触媒とし
て、燃料リーン雰囲気でNOx を吸蔵し、吸蔵されたNO x
を燃料ストイキ〜リッチ雰囲気で放出するNOx 吸蔵材を
用いたNOx 吸蔵還元型の排ガス浄化用触媒が開発されて
いる。
[0003] In this lean burn engine,
Burns in an oxygen-excess fuel-lean condition,
Exhaust gas is reduced in a reducing atmosphere by stoichiometric to rich conditions.
NO as atmospherex Has been developed to reduce and purify
Has been used. And the best catalyst for this system
NO in fuel lean atmospherex And occluded NO x 
To release NOx in fuel stoichiometric rich atmospherex Occlusion material
NO usedx A storage reduction type exhaust gas purification catalyst has been developed
I have.

【0004】例えば特開平5-317652号公報には、Baなど
のアルカリ土類金属とPtをγ-Al2O3などの多孔質酸化物
担体に担持した排ガス浄化用触媒が提案されている。ま
た特開平 6-31139号公報には、Kなどのアルカリ金属と
Ptをγ-Al2O3などの多孔質酸化物担体に担持した排ガス
浄化用触媒が提案されている。さらに特開平5-168860号
公報には、Laなどの希土類元素とPtをγ-Al2O3などの多
孔質酸化物担体に担持した排ガス浄化用触媒が提案され
ている。
For example, Japanese Patent Application Laid-Open No. Hei 5-317652 proposes an exhaust gas purifying catalyst in which an alkaline earth metal such as Ba and Pt are supported on a porous oxide carrier such as γ-Al 2 O 3 . Also, JP-A-6-31139 discloses that an alkali metal such as K is used.
An exhaust gas purifying catalyst in which Pt is supported on a porous oxide carrier such as γ-Al 2 O 3 has been proposed. Further, Japanese Patent Application Laid-Open No. 5-168860 proposes an exhaust gas purifying catalyst in which a rare earth element such as La and Pt are supported on a porous oxide carrier such as γ-Al 2 O 3 .

【0005】このNOx 吸蔵還元型触媒を用いれば、空燃
比を燃料リーン側からパルス状に燃料ストイキ〜リッチ
側となるように制御することにより、排ガスもリーン雰
囲気からパルス状にストイキ〜リッチ雰囲気となる。し
たがって、リーン側ではNOxがNOx 吸蔵材に吸蔵され、
それがストイキ〜リッチ側で放出されて排ガス中に多量
に含まれる炭化水素(HC)や一酸化炭素(CO)などの還
元性成分と反応して浄化されるため、リーンバーンエン
ジンからの排ガスであってもNOx を効率良く浄化するこ
とができる。また排ガス中のHC及びCOは、貴金属により
酸化されるとともにNOx の還元にも消費されるので、HC
及びCOも効率よく浄化される。
[0005] By using this NO x storage-and-reduction type catalyst, by controlling the air-fuel ratio so that the fuel stoichiometric-rich side of the fuel lean side in a pulsed manner, the stoichiometric-rich atmosphere exhaust gas from a lean atmosphere pulsed Becomes Therefore, on the lean side, NO x is stored in the NO x storage material,
It is released on the stoichiometric to rich side and is purified by reacting with reducing components such as hydrocarbons (HC) and carbon monoxide (CO) contained in the exhaust gas in large amounts. can efficiently purify NO x even. The HC and CO in the exhaust gas, since it is consumed in the reduction of the NO x while being oxidized by the noble metal, HC
And CO is also purified efficiently.

【0006】[0006]

【発明が解決しようとする課題】ところで自動車用の排
ガス浄化用触媒では、自動車の排ガス流路内に安定して
保持し、排ガスと触媒成分との接触面積を高めるととも
に、圧損の増大を極力抑制する必要がある。そこで従来
より、コーディエライトなどの MgO・ Al2O3・SiO2複合
酸化物から形成されたハニカム形状の基材が用いられ、
この基材の表面に触媒成分を担持した多孔質担体よりな
るコート層を形成したモノリス触媒が多く用いられてい
る。
In an exhaust gas purifying catalyst for an automobile, the catalyst is stably held in an exhaust gas flow passage of the automobile, the contact area between the exhaust gas and the catalyst component is increased, and an increase in pressure loss is suppressed as much as possible. There is a need to. Therefore, conventionally, a honeycomb-shaped substrate formed of MgO / Al 2 O 3 / SiO 2 composite oxide such as cordierite has been used,
A monolith catalyst having a coat layer formed of a porous carrier carrying a catalyst component formed on the surface of the substrate is often used.

【0007】ところがNOx 吸蔵還元型のモノリス触媒に
おいて、NOx 吸蔵材としてアルカリ金属を用いたもので
は、使用中に基材の劣化が生じ、三元触媒など他の触媒
に比べて耐熱衝撃性などの強度が低下することが明らか
となった。そのため交換の頻度を高める必要があり、単
位使用時間当たりのコストが高いという不具合がある。
[0007] However in the NO x storage reduction type monolithic catalyst, one using an alkali metal as the NO x storage material, degradation of the substrate occurs during use, thermal shock resistance as compared with other catalysts such as three-way catalyst It was clarified that the strength of such as decreased. Therefore, it is necessary to increase the frequency of replacement, and there is a problem that the cost per unit usage time is high.

【0008】本発明はこのような事情に鑑みてなされた
ものであり、基材の劣化を抑制することで耐熱衝撃性な
どの強度の低下を防止することを目的とする。
The present invention has been made in view of such circumstances, and an object of the present invention is to prevent deterioration in strength such as thermal shock resistance by suppressing deterioration of a substrate.

【0009】[0009]

【課題を解決するための手段】上記課題を解決する本発
明の排ガス浄化用触媒の特徴は、SiO2を組成中に含む基
材と、基材の表面に形成され少なくとも貴金属とアルカ
リ金属とを担持した多孔質担体よりなるコート層と、か
らなる排ガス浄化用触媒であって、基材中のSiO2含有量
を基材全体の50〜65重量%としたことにある。
The feature of the exhaust gas purifying catalyst of the present invention that solves the above-mentioned problems is that a base material containing SiO 2 in its composition and at least a noble metal and an alkali metal formed on the surface of the base material are used. An exhaust gas purifying catalyst comprising a coat layer formed of a supported porous carrier, wherein the content of SiO 2 in the substrate is set to 50 to 65% by weight of the entire substrate.

【0010】[0010]

【発明の実施の形態】本願発明者らは、基材の劣化原因
について鋭意研究したところ、組成中にSiO2を含む基材
で劣化が生じることを見出した。すなわち MgO・ Al2O3
・SiO2複合酸化物からなる構造体を基材とし、貴金属と
アルカリ金属を担持したNOx 吸蔵還元型の排ガス浄化用
触媒では、アルカリ金属を含まないものに比べて熱膨張
係数が高くなることが明らかとなった。熱膨張係数が高
くなると、耐熱衝撃性が低下して強度が低下する。
BEST MODE FOR CARRYING OUT THE INVENTION The inventors of the present application have conducted intensive studies on the causes of deterioration of a base material, and have found that deterioration occurs in a base material containing SiO 2 in the composition. That is, MgO ・ Al 2 O 3
A NO x storage reduction type exhaust gas purification catalyst that uses a structure made of SiO 2 composite oxide as a base material and carries a noble metal and an alkali metal has a higher thermal expansion coefficient than one that does not contain an alkali metal Became clear. When the coefficient of thermal expansion increases, the thermal shock resistance decreases and the strength decreases.

【0011】そして上記不具合が生じた触媒中のアルカ
リ金属の担持分布を調査したところ、基材中にもアルカ
リ金属が存在していたことから、このようになる原因と
しては、基材中のSiO2成分とアルカリ金属との反応によ
ってガラス相が形成されることでSiO2が消費され、コー
ト層と基材との界面から優先的に反応が生じて複合酸化
物組成が変化してしまうことにあることが解明された。
When the distribution of the alkali metal in the catalyst in which the above problem occurred was examined, the alkali metal was also present in the base material. The reaction between the two components and the alkali metal results in the formation of a glass phase, which consumes SiO 2, causing a preferential reaction from the interface between the coat layer and the substrate, resulting in a change in the composite oxide composition. It was revealed.

【0012】そこで本発明では、基材中のSiO2含有量を
基材全体の50〜65重量%としている。このようにSiO2
を多くすることで、アルカリ金属との反応でSiO2が消費
されても MgO・ Al2O3・SiO2複合酸化物の組成を最適な
範囲とすることができる。したがって強度の低下が抑制
され、むしろ反応によって強度が向上する場合もある。
Therefore, in the present invention, the content of SiO 2 in the substrate is set to 50 to 65% by weight of the whole substrate. By increasing the amount of SiO 2 in this manner, the composition of the MgO.Al 2 O 3 .SiO 2 composite oxide can be set to an optimum range even when SiO 2 is consumed in the reaction with the alkali metal. Therefore, a decrease in strength is suppressed, and in some cases, the strength is improved by a reaction.

【0013】SiO2を組成中に含む基材としては、 MgO・
Al2O3・SiO2系複合酸化物、 Si3N4、 SiCなどが例示さ
れるが、耐熱性、コストに特に優れた MgO・ Al2O3・Si
O2系複合酸化物が望ましく、コーディエライトが特に好
ましく用いられる。
As a substrate containing SiO 2 in its composition, MgO
Al 2 O 3 · SiO 2 composite oxide, Si 3 N 4, but such as SiC is exemplified, heat resistance, particularly excellent MgO · Al 2 O 3 · Si cost
O 2 -based composite oxides are desirable, and cordierite is particularly preferably used.

【0014】本発明では、この基材のSiO2含有量を基材
全体の50〜65重量%としている。SiO2含有量が50重量%
より少ないと、アルカリ金属との反応によって熱膨張係
数が高くなってしまい強度に不足する。またNOx 吸蔵還
元型の排ガス浄化用触媒におけるアルカリ金属の担持量
は、基材1リットル当たり多くても2モルであるので、
SiO2含有量の上限は65重量%で十分である。そして65重
量%より多くしても、理由は不明であるが熱膨張係数が
高くなって強度に不足するようになる。
In the present invention, the SiO 2 content of the substrate is set to 50 to 65% by weight of the whole substrate. SiO 2 content is 50% by weight
If the amount is smaller, the coefficient of thermal expansion increases due to the reaction with the alkali metal, resulting in insufficient strength. In addition, the amount of alkali metal carried in the NO x storage reduction type exhaust gas purifying catalyst is at most 2 mol per liter of the base material.
An upper limit of the SiO 2 content of 65% by weight is sufficient. If the content is more than 65% by weight, the coefficient of thermal expansion becomes high and the strength becomes insufficient, although the reason is unknown.

【0015】この基材の形状は、ハニカム形状、発泡体
などの多孔質形状、網状、ペレット状など排ガスとの接
触面積が大きなものであれば特に制限されない。また金
属箔などから形成された基体に上記基材の粉末をコート
したものを基材とすることもできる。
The shape of the substrate is not particularly limited as long as it has a large contact area with the exhaust gas, such as a honeycomb shape, a porous shape such as a foam, a net shape, and a pellet shape. A substrate obtained by coating a substrate formed of a metal foil or the like with a powder of the above substrate can also be used as the substrate.

【0016】コート層は、多孔質担体と、多孔質担体に
担持された少なくとも貴金属とアルカリ金属とから構成
される。多孔質担体としては、 Al2O3、ZrO2、TiO2、Ce
O2などから種々選択して用いることができる。これらの
酸化物を単独で用いてもよいし、複数種類混合して用い
てもよく、複数種の複合酸化物として用いることもでき
る。例えば触媒活性の点からは少なくとも Al2O3を含む
ことが好ましく、TiO2を混合すれば耐硫黄被毒性が向上
する。またCeO2あるいはCeO2−ZrO2固溶体を混合すれ
ば、その酸素吸蔵放出能により浄化活性が向上する。
The coating layer comprises a porous carrier, and at least a noble metal and an alkali metal supported on the porous carrier. Al 2 O 3 , ZrO 2 , TiO 2 , Ce
Various types such as O 2 can be used. These oxides may be used alone, or two or more kinds may be mixed and used as a plurality of kinds of composite oxides. For example, from the viewpoint of catalytic activity, it is preferable to contain at least Al 2 O 3. If TiO 2 is mixed, the sulfur poisoning resistance is improved. If CeO 2 or CeO 2 —ZrO 2 solid solution is mixed, the purification activity is improved by its oxygen storage / release ability.

【0017】貴金属としては、Pt,Rh,Pd,Ir,Ruなど
から選択して用いることができる。このうち一種でもよ
いし、複数種類を担持することもできる。その担持量
は、触媒1リットル当たり 0.1〜20重量%程度が好まし
い。
The noble metal can be selected from Pt, Rh, Pd, Ir, Ru and the like. Of these, one type may be used, or a plurality of types may be supported. The supporting amount is preferably about 0.1 to 20% by weight per liter of the catalyst.

【0018】アルカリ金属としてはK、Na、Csなどが例
示される。アルカリ金属の担持量は、触媒1リットル当
たり0.01〜 1.0モルの範囲が好ましい。この範囲より少
ないとNOx 吸蔵能が低く、この範囲を超えて担持すると
基材成分との反応確率が高くなって基材の強度に不足す
るようになる。
Examples of the alkali metal include K, Na and Cs. The loading amount of the alkali metal is preferably in the range of 0.01 to 1.0 mol per liter of the catalyst. If the amount is less than this range, the NO x storage ability is low, and if the amount exceeds this range, the probability of reaction with the base material component increases and the strength of the base material becomes insufficient.

【0019】またNOx 吸蔵還元型触媒の場合には、アル
カリ金属に加えてアルカリ土類金属及び希土類元素の少
なくとも一方を担持することも好ましい。アルカリ土類
金属としてはBa、Be、Ca、Mg、Srなどが例示される。ま
た希土類元素としてはSc,Y,La,Yb,Nd,Smなどが例
示される。なおアルカリ土類金属及び希土類元素はSiO2
とは反応しないので、従来と同様に触媒1リットル当た
り 0.1〜2モルとするのが好ましい。
In the case of the NO x storage reduction catalyst, it is preferable that at least one of an alkaline earth metal and a rare earth element is supported in addition to the alkali metal. Examples of the alkaline earth metal include Ba, Be, Ca, Mg, Sr and the like. Examples of rare earth elements include Sc, Y, La, Yb, Nd, and Sm. The alkaline earth metal and the rare earth element are SiO 2
Is not reacted with, so that it is preferably 0.1 to 2 mol per liter of the catalyst as in the prior art.

【0020】なお本発明の排ガス浄化用触媒は、コート
層にアルカリ金属を含むものであればよく、NOx 吸蔵還
元型触媒、NOx 吸収触媒、あるいは場合によっては三元
触媒、酸化触媒などとして用いることができる。
[0020] Note that the exhaust gas purifying catalyst of the present invention may be those containing an alkali metal to the coating layer, NO x storage reduction catalyst, NO x absorbent catalyst or three-way catalyst optionally, as such an oxidation catalyst Can be used.

【0021】[0021]

【実施例】以下、実施例により本発明を具体的に説明す
る。
The present invention will be described below in detail with reference to examples.

【0022】(実施例1)SiO2粉末を51重量%、MgO 粉
末を14重量%、 Al2O3粉末を35重量%含む混合粉末を混
合し、1300〜1400℃で焼成して MgO・ Al2O3・SiO2系複
合酸化物を調製した。この複合酸化物はコーディエライ
トに分類される。この複合酸化物を粉砕した粉末を水及
びバインダと混合してペースト状とし、ハニカム形状に
押出成形後1400℃で焼成してハニカム基材を形成した。
Example 1 A mixed powder containing 51% by weight of SiO 2 powder, 14% by weight of MgO powder, and 35% by weight of Al 2 O 3 powder was mixed, and calcined at 1300 to 1400 ° C. to obtain MgO · Al. A 2 O 3 · SiO 2 composite oxide was prepared. This composite oxide is classified as cordierite. The powder obtained by pulverizing the composite oxide was mixed with water and a binder to form a paste, extruded into a honeycomb shape, and fired at 1400 ° C. to form a honeycomb substrate.

【0023】一方、 Al2O3粉末 100重量部と、TiO2粉末
100重量部と、CeO2−ZrO2固溶体粉末30重量部とをアル
ミナゾルとともに蒸留水中に分散させたスラリーを調製
し、上記ハニカム基材を浸漬後引き上げ、乾燥・焼成し
てハニカム基材表面にコート層を形成した。コート層は
ハニカム基材1リットル当たり 230g形成され、その厚
さは 100〜 200μmである。
On the other hand, 100 parts by weight of Al 2 O 3 powder and TiO 2 powder
Prepare a slurry in which 100 parts by weight and 30 parts by weight of CeO 2 -ZrO 2 solid solution powder were dispersed in distilled water together with alumina sol, dipped the above honeycomb substrate, pulled up, dried and fired to coat the honeycomb substrate surface A layer was formed. The coating layer is formed at 230 g per liter of the honeycomb substrate, and has a thickness of 100 to 200 μm.

【0024】次に、所定濃度のジニトロジアンミン白金
水溶液中にコート層をもつハニカム基材を浸漬し、引き
上げて余分な液滴を吹き払った後、大気中にて室温で乾
燥しPtを吸着担持した。Ptの担持量は、ハニカム基材1
リットル当たり2gである。
Next, the honeycomb substrate having the coating layer is immersed in an aqueous solution of dinitrodiammine platinum having a predetermined concentration, pulled up and blown off excess droplets, and then dried in the air at room temperature to adsorb and carry Pt. did. The supported amount of Pt is the honeycomb substrate 1
2 g per liter.

【0025】さらに所定濃度の酢酸バリウム水溶液の所
定量をコート層に含浸させ、蒸発・乾固後、大気中にて
300℃で1時間焼成してBaを担持した。Baの担持量はハ
ニカム基材1リットル当たり 0.2モルである。次いで所
定濃度の酢酸カリウムが溶解した水溶液の所定量を含浸
させ、蒸発・乾固後、大気中にて 300℃で1時間焼成し
てKを担持してNOx 吸蔵還元型の排ガス浄化用触媒を調
製した。Kの担持量はハニカム基材1リットル当たり
0.2モルである。
Further, a predetermined amount of an aqueous solution of barium acetate having a predetermined concentration is impregnated into the coat layer, and after evaporating to dryness, in the air
Baking was carried out at 300 ° C. for 1 hour to carry Ba. The supported amount of Ba is 0.2 mol per liter of the honeycomb substrate. Subsequently, a predetermined amount of an aqueous solution in which a predetermined concentration of potassium acetate is dissolved is impregnated, evaporated and dried, and then calcined at 300 ° C. for one hour in the air to carry K and carry a NO x storage reduction type exhaust gas purifying catalyst. Was prepared. The amount of K supported per liter of honeycomb substrate
0.2 mol.

【0026】(実施例2)MgO・ Al2O3・SiO2系複合酸
化物中のSiO2含有量を54重量%としたこと以外は実施例
1と同様にしてハニカム基材を調製し、実施例1と同様
にしてNOx 吸蔵還元型の排ガス浄化用触媒を調製した。
Example 2 A honeycomb substrate was prepared in the same manner as in Example 1 except that the content of SiO 2 in the MgO.Al 2 O 3 .SiO 2 based composite oxide was 54% by weight. It was prepared NO x storage-and-reduction type exhaust gas purifying catalyst in the same manner as in example 1.

【0027】(実施例3)MgO・ Al2O3・SiO2系複合酸
化物中のSiO2含有量を58重量%としたこと以外は実施例
1と同様にしてハニカム基材を調製し、実施例1と同様
にしてNOx 吸蔵還元型の排ガス浄化用触媒を調製した。
Example 3 A honeycomb substrate was prepared in the same manner as in Example 1 except that the content of SiO 2 in the MgO.Al 2 O 3 .SiO 2 composite oxide was 58% by weight. It was prepared NO x storage-and-reduction type exhaust gas purifying catalyst in the same manner as in example 1.

【0028】(実施例4)MgO・ Al2O3・SiO2系複合酸
化物中のSiO2含有量を62重量%としたこと以外は実施例
1と同様にしてハニカム基材を調製し、実施例1と同様
にしてNOx 吸蔵還元型の排ガス浄化用触媒を調製した。
Example 4 A honeycomb substrate was prepared in the same manner as in Example 1 except that the SiO 2 content in the MgO.Al 2 O 3 .SiO 2 -based composite oxide was changed to 62% by weight. It was prepared NO x storage-and-reduction type exhaust gas purifying catalyst in the same manner as in example 1.

【0029】(比較例1)MgO・ Al2O3・SiO2系複合酸
化物中のSiO2含有量を49重量%としたこと以外は実施例
1と同様にしてハニカム基材を調製し、実施例1と同様
にしてNOx 吸蔵還元型の排ガス浄化用触媒を調製した。
このハニカム基材の組成は、従来広く用いられているコ
ーディエライト組成である。
Comparative Example 1 A honeycomb substrate was prepared in the same manner as in Example 1 except that the content of SiO 2 in the MgO.Al 2 O 3 .SiO 2 -based composite oxide was 49% by weight. It was prepared NO x storage-and-reduction type exhaust gas purifying catalyst in the same manner as in example 1.
The composition of the honeycomb substrate is a cordierite composition which has been widely used in the past.

【0030】(比較例2)MgO・ Al2O3・SiO2系複合酸
化物中のSiO2含有量を45重量%としたこと以外は実施例
1と同様にしてハニカム基材を調製し、実施例1と同様
にしてNOx 吸蔵還元型の排ガス浄化用触媒を調製した。
Comparative Example 2 A honeycomb substrate was prepared in the same manner as in Example 1 except that the content of SiO 2 in the MgO.Al 2 O 3 .SiO 2 based composite oxide was 45% by weight. It was prepared NO x storage-and-reduction type exhaust gas purifying catalyst in the same manner as in example 1.

【0031】(比較例3)MgO・ Al2O3・SiO2系複合酸
化物中のSiO2含有量を70重量%としたこと以外は実施例
1と同様にしてハニカム基材を調製し、実施例1と同様
にしてNOx 吸蔵還元型の排ガス浄化用触媒を調製した。
Comparative Example 3 A honeycomb substrate was prepared in the same manner as in Example 1 except that the content of SiO 2 in the MgO.Al 2 O 3 .SiO 2 -based composite oxide was 70% by weight. It was prepared NO x storage-and-reduction type exhaust gas purifying catalyst in the same manner as in example 1.

【0032】<試験・評価>得られたそれぞれの触媒に
ついて、ハニカム基材の熱膨張係数をによって測定し
た。各ハニカム基材のSiO2含有量を横軸に、熱膨張係数
を縦軸に取ってグラフ化した結果を図1に示す。
<Test / Evaluation> For each of the obtained catalysts, the coefficient of thermal expansion of the honeycomb substrate was measured. FIG. 1 shows the results obtained by plotting the SiO 2 content of each honeycomb substrate on the horizontal axis and the thermal expansion coefficient on the vertical axis.

【0033】図1より、基材のSiO2含有量が50〜65重量
%の範囲にあれば熱膨張係数が2×10-6/℃未満とな
り、この範囲であれば耐熱衝撃性が従来より改善された
範囲となる。しかしSiO2含有量がこの範囲にない比較例
の触媒では、熱膨張係数が高くなって自動車用の排ガス
浄化用触媒としては耐熱衝撃性に不足している。
FIG. 1 shows that when the SiO 2 content of the substrate is in the range of 50 to 65% by weight, the coefficient of thermal expansion is less than 2 × 10 −6 / ° C. An improved range. However, the catalyst of Comparative Example in which the SiO 2 content is not in this range has a high thermal expansion coefficient and is insufficient in thermal shock resistance as an exhaust gas purifying catalyst for automobiles.

【0034】[0034]

【発明の効果】すなわち本発明の排ガス浄化用触媒によ
れば、担持成分としてアルカリ金属を用いても基材の耐
熱衝撃性が低くなるような不具合がないので、劣化まで
の使用期間を長くすることができ、単位使用時間当たり
のコストを低減することができる。
According to the exhaust gas purifying catalyst of the present invention, even when an alkali metal is used as a carrier component, there is no problem that the thermal shock resistance of the base material is lowered, so that the use period until the deterioration is extended. And cost per unit usage time can be reduced.

【図面の簡単な説明】[Brief description of the drawings]

【図1】SiO2含有割合と熱膨張係数との関係を示すグラ
フである。
FIG. 1 is a graph showing a relationship between a SiO 2 content ratio and a coefficient of thermal expansion.

フロントページの続き Fターム(参考) 3G091 AA02 AB06 BA10 BA14 BA39 GA06 GB01X GB02W GB03W GB04W GB04X GB05W GB06W GB07W GB10X GB17X 4D048 AA06 AB02 AB07 BA01X BA03X BA06X BA07X BA08X BA14X BA15X BA19X BA30X BA31Y BA32Y BA33Y BA42X BB02 EA04 4G069 AA03 AA08 BA01A BA01B BA02A BA02B BA04B BA06A BA06B BA13A BA13B BA20A BA20B BB02A BB02B BB04A BB04B BB06B BC01A BC02A BC03A BC03B BC06A BC09A BC10A BC11A BC12A BC13A BC13B BC43B BC51B BC69A BC70A BC71A BC72A BC74A BC75A BC75B CA03 CA08 CA13 EA19 FA06 FB15 FC08Continued on the front page F-term (reference) 3G091 AA02 AB06 BA10 BA14 BA39 GA06 GB01X GB02W GB03W GB04W GB04X GB05W GB06W GB07W GB10X GB17X 4D048 AA06 AB02 AB07 BA01X BA03X BA06X BA07X BA08X BA14X BA15X BA19A BAY ABAY ABAY BAY ABAY BAY BAY XA BA02A BA02B BA04B BA06A BA06B BA13A BA13B BA20A BA20B BB02A BB02B BB04A BB04B BB06B BC01A BC02A BC03A BC03B BC06A BC09A BC10A BC11A BC12A BC13A BC13B BC43B BC51B BC69A BC70 BC07ABC08A

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 SiO2を組成中に含む基材と、該基材の表
面に形成され少なくとも貴金属とアルカリ金属とを担持
した多孔質担体よりなるコート層と、からなる排ガス浄
化用触媒であって、 該基材中のSiO2含有量を該基材全体の50〜65重量%とし
たことを特徴とする排ガス浄化用触媒。
An exhaust gas purifying catalyst comprising: a base material containing SiO 2 in a composition; and a coat layer formed on the surface of the base material and formed of a porous support supporting at least a noble metal and an alkali metal. An exhaust gas purifying catalyst, wherein the content of SiO 2 in the substrate is 50 to 65% by weight of the entire substrate.
JP2000290643A 2000-09-25 2000-09-25 Exhaust gas cleaning catalyst Pending JP2002095967A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000290643A JP2002095967A (en) 2000-09-25 2000-09-25 Exhaust gas cleaning catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000290643A JP2002095967A (en) 2000-09-25 2000-09-25 Exhaust gas cleaning catalyst

Publications (1)

Publication Number Publication Date
JP2002095967A true JP2002095967A (en) 2002-04-02

Family

ID=18773844

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000290643A Pending JP2002095967A (en) 2000-09-25 2000-09-25 Exhaust gas cleaning catalyst

Country Status (1)

Country Link
JP (1) JP2002095967A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008066197A1 (en) * 2006-12-01 2008-06-05 Toyota Jidosha Kabushiki Kaisha Exhaust gas clean-up apparatus
EP2236194A1 (en) * 2009-03-31 2010-10-06 Ibiden Co., Ltd. Honeycomb structure

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008066197A1 (en) * 2006-12-01 2008-06-05 Toyota Jidosha Kabushiki Kaisha Exhaust gas clean-up apparatus
US8128881B2 (en) 2006-12-01 2012-03-06 Toyota Jidosha Kabushiki Kaisha Exhaust-gas converting apparatus
KR101159901B1 (en) 2006-12-01 2012-06-25 이비덴 가부시키가이샤 Exhaust-gas converting apparatus
CN101547734B (en) * 2006-12-01 2012-09-05 丰田自动车株式会社 Exhaust gas clean-up apparatus
EP2236194A1 (en) * 2009-03-31 2010-10-06 Ibiden Co., Ltd. Honeycomb structure

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