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JPH07132226A - Catalyst for purifying exhaust gas - Google Patents

Catalyst for purifying exhaust gas

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Publication number
JPH07132226A
JPH07132226A JP5281177A JP28117793A JPH07132226A JP H07132226 A JPH07132226 A JP H07132226A JP 5281177 A JP5281177 A JP 5281177A JP 28117793 A JP28117793 A JP 28117793A JP H07132226 A JPH07132226 A JP H07132226A
Authority
JP
Japan
Prior art keywords
catalyst
nox
metal
exhaust gas
carrier
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
JP5281177A
Other languages
Japanese (ja)
Inventor
Hiroshi Hirayama
洋 平山
Masaru Ishii
勝 石井
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 JP5281177A priority Critical patent/JPH07132226A/en
Publication of JPH07132226A publication Critical patent/JPH07132226A/en
Pending legal-status Critical Current

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

Abstract

PURPOSE:To improve both purifying performance and durability at a low temp. in the subject catalyst carrying a noble metal catalyst and a NOx absorbing metal. CONSTITUTION:This catalyst is composed of a honeycomb carrier 1, the noble metal catalyst 3 deposited uniformly in an axis direction of the carrier and the NOx absorbing metal 4 consisting of at least either alkaline earth metal or alkali metal and being deposited so as to have a concn. distribution in the axis direction of the carrier. Both NOx-absorbing function due to the NO. absorbing metal and ternary catalyst function due to the noble metal catalyst are surely exhibited.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は排気ガス浄化用触媒に関
し、詳しくは、排ガス中に含まれる一酸化炭素(CO)
や炭化水素(HC)を酸化するのに必要な量より過剰な
酸素が含まれている排気ガス中の、窒素酸化物(NO
x)を効率よく浄化できる排気ガス浄化用触媒及びその
製造方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying catalyst, and more specifically, carbon monoxide (CO) contained in exhaust gas.
Nitrogen oxides (NO) in exhaust gas that contain excess oxygen than that required to oxidize hydrocarbons and hydrocarbons (HC).
The present invention relates to an exhaust gas purification catalyst that can efficiently purify x) and a method for manufacturing the same.

【0002】[0002]

【従来の技術】従来より、自動車の排気ガス浄化用触媒
として、CO及びHCの酸化とNOxの還元とを同時に
行って排気ガスを浄化する三元触媒が用いられている。
このような触媒としては、例えばコージェライトなどの
耐熱性担体にγ−アルミナからなる担持層を形成し、そ
の担持層にPt,Pd,Rhなどの貴金属触媒を担持さ
せたものが広く知られている。
2. Description of the Related Art Conventionally, a three-way catalyst for purifying exhaust gas by simultaneously oxidizing CO and HC and reducing NOx has been used as a catalyst for purifying exhaust gas of an automobile.
As such a catalyst, for example, a catalyst in which a supporting layer made of γ-alumina is formed on a heat-resistant carrier such as cordierite and a noble metal catalyst such as Pt, Pd, Rh is supported on the supporting layer is widely known. There is.

【0003】ところで、このような排気ガス浄化用触媒
の浄化性能は、エンジンの空燃比(A/F)によって大
きく異なる。すなわち、空燃比の大きい、つまり燃料濃
度が希薄なリーン側では排気ガス中の酸素量が多くな
り、COやHCを浄化する酸化反応が活発である反面N
Oxを浄化する還元反応が不活発になる。逆に空燃比の
小さい、つまり燃料濃度が濃いリッチ側では排気ガス中
の酸素量が少なくなり、酸化反応は不活発となるが還元
反応は活発になる。
By the way, the purification performance of such an exhaust gas purification catalyst greatly differs depending on the air-fuel ratio (A / F) of the engine. That is, on the lean side where the air-fuel ratio is large, that is, where the fuel concentration is lean, the amount of oxygen in the exhaust gas is large, and the oxidation reaction for purifying CO and HC is active, but N
The reduction reaction for purifying Ox becomes inactive. On the contrary, on the rich side where the air-fuel ratio is small, that is, where the fuel concentration is high, the amount of oxygen in the exhaust gas is small, and the oxidation reaction becomes inactive but the reduction reaction becomes active.

【0004】一方、自動車の走行において、市街地走行
の場合には加速・減速が頻繁に行われ、空燃比はストイ
キ(理論空燃比)近傍からリッチ状態までの範囲内で頻
繁に変化する。このような走行における低燃費化の要請
に応えるには、なるべく酸素過剰の混合気を供給するリ
ーン側での運転が必要となる。また、加速減速に伴う過
渡域において数秒程度の細かいリーンパルスが発生する
ことが知られており、このリーンパルスにおいて未浄化
のNOxが多く排出されることもわかっている。したが
ってリーン側(リーンパルス)においてもNOxを十分
に浄化できる触媒の開発が望まれている。
On the other hand, when driving an automobile, acceleration and deceleration are frequently performed in urban areas, and the air-fuel ratio frequently changes within the range from near stoichiometric (theoretical air-fuel ratio) to the rich state. In order to meet the demand for low fuel consumption in such traveling, it is necessary to operate on the lean side to supply an air-fuel mixture with excess oxygen as much as possible. Further, it is known that a fine lean pulse of about several seconds is generated in a transitional region accompanying acceleration / deceleration, and it is also known that a large amount of unpurified NOx is discharged in this lean pulse. Therefore, it is desired to develop a catalyst that can sufficiently purify NOx even on the lean side (lean pulse).

【0005】そこで本願出願人は、先にアルカリ土類金
属とPtを担持した触媒を提案している(特願平4−1
30904号)。この触媒によれば、NOxはアルカリ
土類金属に吸収され、それがHCなどの還元性ガスと反
応して浄化されるため、リーン側においてもNOxの浄
化性能に優れている。特願平4−130904号に開示
された触媒では、例えばバリウムが単独酸化物として担
体に担持され、それがNOxと反応して硝酸バリウム
(Ba(NO32 )を生成することでNOxを吸着す
るものと考えられている。
Therefore, the applicant of the present application has previously proposed a catalyst carrying an alkaline earth metal and Pt (Japanese Patent Application No. 4-1).
30904). According to this catalyst, NOx is absorbed by the alkaline earth metal and is reacted with a reducing gas such as HC to be purified, so that the lean side is also excellent in the purification performance of NOx. In the catalyst disclosed in Japanese Patent Application No. 4-130904, for example, barium is supported on a carrier as a single oxide, and it reacts with NOx to generate barium nitrate (Ba (NO 3 ) 2 ) to generate NOx. It is considered to adsorb.

【0006】また特開平3−106446号公報にも、
バリウムとPdとを共存担持した排気ガス浄化用触媒が
開示されている。
Further, in Japanese Patent Laid-Open No. 3-106446,
An exhaust gas purifying catalyst carrying coexisting barium and Pd is disclosed.

【0007】[0007]

【発明が解決しようとする課題】ところが、従来の三元
触媒にアルカリ土類金属などのNOx吸収作用をもつ元
素を添加すると、初期のNOx浄化性能は極めて優れた
ものとなるが、耐久性が悪いという問題があった。また
低温時の浄化性能が低いという問題があることも明らか
となった。
However, when an element having an NOx absorbing action such as an alkaline earth metal is added to the conventional three-way catalyst, the initial NOx purification performance is extremely excellent, but the durability is low. There was a problem of being bad. It was also revealed that there is a problem that the purification performance at low temperatures is low.

【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、貴金属触媒とNOx吸収金属とを担持した
排気ガス浄化用触媒において、低温時の浄化性能と耐久
性の両方を向上させることを目的とする。
The present invention has been made in view of the above circumstances, and it is an object of the present invention to improve both the purification performance and durability at low temperature in an exhaust gas purification catalyst carrying a noble metal catalyst and a NOx absorbing metal. With the goal.

【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
明の排気ガス浄化用触媒は、多孔質体からなり軸方向に
延びるハニカム通路をもつ担体と、担体の軸方向に均一
に担持された貴金属触媒と、アルカリ土類金属及びアル
カリ金属の少なくとも一方からなり担体の軸方向に濃度
分布をもって担持されたNOx吸収金属と、からなるこ
とを特徴とする。
The exhaust gas purifying catalyst of the present invention for solving the above-mentioned problems is a carrier which is made of a porous body and has a honeycomb passage extending in the axial direction, and is uniformly supported in the axial direction of the carrier. It is characterized by comprising a noble metal catalyst and a NOx absorbing metal which is composed of at least one of an alkaline earth metal and an alkali metal and has a concentration distribution in the axial direction of the carrier.

【0010】多孔質体からなる担体としては、コージェ
ライトなどから形成されたハニカム体にアルミナなどの
担持層が被覆されたモノリス担体、金属平板と波板が交
互に積層されそれにアルミナなどの担持層が被覆された
メタル担体など、従来と同様のものが用いられる。貴金
属触媒としてはPt,Pd,Rhがあり、その担持量は
担体1リットル当たり1g〜2gが好ましい。1gより
少ないと浄化性能が低く、2gより多くしても効果が飽
和してコストだけが高くなる。この貴金属触媒は担体の
軸方向全長にわたって均一に担持されている。
As the carrier made of a porous body, a monolith carrier in which a carrier body made of cordierite or the like is coated with a carrier layer made of alumina or the like, and metal flat plates and corrugated plates are alternately laminated on the carrier body made of alumina or the like. A conventional metal carrier such as a metal carrier coated with is used. Noble metal catalysts include Pt, Pd, and Rh, and the supported amount thereof is preferably 1 g to 2 g per liter of the carrier. If it is less than 1 g, the purification performance is low, and if it is more than 2 g, the effect is saturated and only the cost is increased. The noble metal catalyst is uniformly supported on the entire length of the carrier in the axial direction.

【0011】アルカリ土類金属としては、Ca,Sr,
Baなどが用いられ、アルカリ金属としてはLi,N
a,Kなどが用いられる。これらの1種でもよいし2種
以上を共存担持することもできる。これらの金属はNO
x吸収作用をもつので、NOx吸収金属と称する。この
NOx吸収金属は、担体の軸方向に濃度分布をもって担
持されている。なお、NOx吸収金属の担持量は、担体
1リットル当たり0.1〜0.5モルが好ましい。0.
1より少ないとNOx吸収作用が得られず、0.5より
多くすると貴金属の被覆あるいはアルミナの耐熱性低下
等の不具合がある。
Alkaline earth metals include Ca, Sr,
Ba or the like is used, and alkali metals such as Li and N are used.
a, K, etc. are used. One of these may be used, or two or more of them may be coexistently supported. These metals are NO
Since it has an x-absorbing effect, it is called a NOx absorbing metal. This NOx absorbing metal is carried with a concentration distribution in the axial direction of the carrier. The amount of the NOx absorbing metal supported is preferably 0.1 to 0.5 mol per liter of the carrier. 0.
When it is less than 1, no NOx absorption effect is obtained, and when it is more than 0.5, there is a problem such as coating with a noble metal or reduction in heat resistance of alumina.

【0012】濃度分布の態様としては、例えば上流側半
分又は下流側半分にのみ担持させた構造、あるいは軸方
向の中央部のみに所定幅で担持した構造、あるいは上流
側から下流側へ向かうにつれて担持量が少なくあるいは
多くなるようにした構造など、目的に応じて種々の態様
を選択することができる。NOx吸収金属の担持部分が
約50%程度になるように構成するのが好ましい。
The concentration distribution may be carried out, for example, in a structure in which it is carried only in the upstream half or in the downstream half, in a structure having a predetermined width only in the central portion in the axial direction, or as it goes from the upstream side to the downstream side. Various modes can be selected according to the purpose, such as a structure in which the amount is small or large. It is preferable that the NOx-absorbing metal-supported portion is about 50%.

【0013】なお、このNOx吸収金属は、一般に酸化
物の形で担持されている。
The NOx absorbing metal is generally supported in the form of an oxide.

【0014】[0014]

【作用】本発明者らは、アルカリ土類金属と貴金属触媒
を共存担持した排気ガス浄化用触媒に前記不具合が生じ
る原因について鋭意研究した結果、アルカリ土類金属が
貴金属触媒の活性サイトを減少させ、その結果低温時の
触媒活性が低下することが明らかとなった。
The present inventors have conducted extensive studies on the cause of the above-mentioned problems in the exhaust gas purifying catalyst in which the alkaline earth metal and the precious metal catalyst are co-loaded, and as a result, the alkaline earth metal reduces the active sites of the precious metal catalyst. As a result, it was clarified that the catalyst activity at low temperature decreased.

【0015】また高温時にアルカリ土類金属とアルミナ
とが反応して比表面積が低下するという現象が生じ、そ
れが共存担持された貴金属触媒に直接的に影響するため
耐久性が低下するのであろうと考えられた。そこで本発
明では、貴金属触媒は軸方向に均一に担持させるととも
に、NOx吸収金属は軸方向に濃度分布をもって担持さ
せた。したがってNOx吸収金属が担持されていない部
分、あるいはNOx吸収金属の担持量が少ない部分で
は、NOx吸収金属と貴金属触媒の直接的な接触を回避
でき、貴金属触媒の活性サイトの低下が防止される。そ
して貴金属触媒は従来の三元触媒と同様にHC,COの
酸化とNOxの還元反応を行う。
Further, at a high temperature, there occurs a phenomenon that the alkaline earth metal and alumina react with each other to reduce the specific surface area, which directly affects the coexisting and supported noble metal catalyst, so that the durability may be reduced. it was thought. Therefore, in the present invention, the noble metal catalyst is uniformly loaded in the axial direction, and the NOx absorbing metal is loaded with a concentration distribution in the axial direction. Therefore, direct contact between the NOx absorbing metal and the noble metal catalyst can be avoided in the portion where the NOx absorbing metal is not supported, or in the portion where the NOx absorbing metal is supported in a small amount, and the reduction of the active site of the noble metal catalyst is prevented. Then, the noble metal catalyst performs the oxidation reaction of HC and CO and the reduction reaction of NOx similarly to the conventional three-way catalyst.

【0016】一方、NOx吸収金属が担持された部分で
は、リーン条件下で排気ガス中のNOxはNOx吸収金
属に吸収され、ストイキあるいはリッチ条件下で吸収さ
れていたNOxが放出されると同時に、貴金属触媒によ
りHCやCOと反応して還元浄化される。またたとえN
Ox吸収金属とアルミナとが反応しても、NOx吸収金
属が担持されていない部分、あるいはNOx吸収金属の
担持量が少ない部分では貴金属触媒への直接的な影響が
回避されるので耐熱性が向上し、その結果耐久性が向上
する。
On the other hand, in the portion where the NOx absorbing metal is carried, NOx in the exhaust gas is absorbed by the NOx absorbing metal under lean conditions, and at the same time the NOx absorbed under stoichiometric or rich conditions is released. The precious metal catalyst reacts with HC and CO for reduction and purification. Also N
Even if the Ox absorbing metal reacts with the alumina, in the portion where the NOx absorbing metal is not supported or in the portion where the amount of NOx absorbing metal supported is small, the direct influence on the noble metal catalyst is avoided, so the heat resistance is improved. As a result, durability is improved.

【0017】[0017]

【実施例】以下、実施例及び比較例により本発明を具体
的に説明する。 (実施例1)図1に本発明の一実施例の排気ガス浄化用
触媒の概略断面図を示し、その要部拡大断面図を図2に
示す。この排気ガス浄化用触媒は、担体基材1と、担体
基材1表面に被覆形成されたアルミナコート層2と、ア
ルミナコート層2に担持されたPt及びRhからなる貴
金属触媒3と、担体基材1の一端側端面から軸長の25
%の部分(L)にのみ担持されたバリウムからなるNO
x吸収金属4と、から構成されている。
EXAMPLES The present invention will be specifically described below with reference to Examples and Comparative Examples. (Embodiment 1) FIG. 1 shows a schematic sectional view of an exhaust gas purifying catalyst according to an embodiment of the present invention, and FIG. 2 shows an enlarged sectional view of a main part thereof. This exhaust gas purifying catalyst comprises a carrier base 1, an alumina coat layer 2 formed on the surface of the carrier base 1, a noble metal catalyst 3 made of Pt and Rh supported on the alumina coat 2, and a carrier base. The axial length from the end face of the material 1 is 25
% Consisting of barium supported only in the% portion (L)
and x-absorbing metal 4.

【0018】以下、この排気ガス浄化用触媒を製造した
方法を説明する。なお、以下の例において「部」は特に
ことわらない限り「重量部」を示す。アルミナ粉末10
0部と、アルミナゾル(アルミナ含有率10wt%)1
0部と、40wt%硝酸アルミニウム水溶液60部、酸
化セリウム40部及び水30部を混合し、コーティング
用スラリーを調製した。
The method for producing this exhaust gas purifying catalyst will be described below. In the following examples, "parts" means "parts by weight" unless otherwise specified. Alumina powder 10
0 parts and alumina sol (alumina content 10 wt%) 1
0 parts, 60 parts of 40 wt% aluminum nitrate aqueous solution, 40 parts of cerium oxide and 30 parts of water were mixed to prepare a coating slurry.

【0019】コージェライト質ハニカム担体基材1(体
積1.7l)を水に浸漬し、余分な水を吹き払った後上
記コーティング用スラリーに浸漬し、取り出した後余分
なスラリーを吹き払い、80℃で20分間乾燥後600
℃で1時間焼成してアルミナコート層2を形成した。ア
ルミナコート層2のコート量は、ハニカム担体の体積1
リットル当たり160gである。
The cordierite honeycomb carrier substrate 1 (volume 1.7 l) was dipped in water, and after blowing off excess water, it was dipped in the above-mentioned coating slurry. After taking it out, the excess slurry was blown off. 600 after drying at ℃ for 20 minutes
The alumina coating layer 2 was formed by firing at 1 ° C. for 1 hour. The coating amount of the alumina coat layer 2 is 1 volume of the honeycomb carrier.
It is 160 g per liter.

【0020】上記のようにして得られたハニカム担体
を、所定濃度のジニトロジアンミン白金水溶液に浸漬
し、引き上げて余分な水滴を吹き払った後250°で乾
燥した。次いで所定濃度の塩化ロジウム水溶液に浸漬
し、引き上げて余分な水滴を吹き払った後250°で乾
燥した。これによりハニカム担体1リットル当たりにし
て、Ptが1.5g、Rhが0.3g均一に担持され
た。
The honeycomb carrier obtained as described above was dipped in a dinitrodiammine platinum aqueous solution of a predetermined concentration, pulled up to blow off excess water drops, and then dried at 250 °. Then, it was dipped in a rhodium chloride aqueous solution of a predetermined concentration, pulled up, blown off excess water droplets, and then dried at 250 °. As a result, 1.5 g of Pt and 0.3 g of Rh were uniformly loaded per liter of the honeycomb carrier.

【0021】次に所定濃度の酢酸バリウム水溶液を用意
し、Pt及びRhが担持された上記ハニカム担体の一端
面から軸長の25%の部分(L)を浸漬し、乾燥後60
0℃で1時間焼成して実施例1の排気ガス浄化用触媒と
した。この25%の部分では、Baはハニカム担体1リ
ットル当たり0.3mol担持されている。 (実施例2)Baをハニカム担体の一端面から軸長の5
0%の部分に担持したこと以外は実施例1と同様の構成
である。 (比較例1)Baを担持していないこと以外は実施例1
と同様の構成である。 (比較例2)Baをハニカム担体全体に均一に担持した
こと以外は実施例1と同様の構成である。 (評価)上記4種類の排気ガス浄化用触媒について、エ
ンジンベンチにて初期と耐久後の低温活性と過渡性能を
評価した。その試験方法は以下のとおりであり、結果を
表1に示す。
Next, a barium acetate aqueous solution having a predetermined concentration is prepared, and a portion (L) of 25% of the axial length is immersed from one end face of the above honeycomb carrier carrying Pt and Rh, and after drying 60
The catalyst for exhaust gas purification of Example 1 was obtained by firing at 0 ° C. for 1 hour. In this 25% portion, 0.3 mol of Ba is loaded per liter of the honeycomb carrier. (Embodiment 2) Ba is made to have an axial length of 5 from one end face of the honeycomb carrier.
The structure is the same as that of Example 1 except that it is carried on the 0% portion. (Comparative Example 1) Example 1 except that Ba was not carried.
It has the same configuration as. (Comparative Example 2) The configuration is the same as that of Example 1 except that Ba is uniformly loaded on the entire honeycomb carrier. (Evaluation) With respect to the above four kinds of exhaust gas purifying catalysts, the low temperature activity and the transient performance were evaluated on the engine bench at the initial stage and after the endurance. The test method is as follows, and the results are shown in Table 1.

【0022】低温活性:A/F=14.6(ストイキ)
を維持し、排気ガス温度を200〜400℃まで昇温し
たときのHC,CO,NOxの各々の50%浄化温度を
測定した。 過渡性能:排気ガス温度を400℃に維持し、A/F=
14.6(ストイキ)を30秒間保持した後、A/F=
16.0(リーン)に変化させ10秒間リーン状態を保
持した後、再びA/F=14.6(ストイキ)に戻して
20秒間保持し、1分間のNOx浄化率(平均)を測定
した。
Low temperature activity: A / F = 14.6 (stoichiometric)
Was maintained, and the 50% purification temperature of each of HC, CO, and NOx when the exhaust gas temperature was raised to 200 to 400 ° C. was measured. Transient performance: Maintain exhaust gas temperature at 400 ° C, A / F =
After holding 14.6 (stoichi) for 30 seconds, A / F =
After changing to 16.0 (lean) and holding the lean state for 10 seconds, the A / F = 14.6 (stoichi) was returned again and held for 20 seconds, and the NOx purification rate (average) for 1 minute was measured.

【0023】耐久試験:排気量2lのエンジンの排気系
に取り付け、排気ガス温度800℃、A/F=14.6
(ストイキ)の条件で50時間運転し、その後上記試験
を行った。 なお、実施例の排気ガス浄化用触媒については、Ba担
持部分が排気ガスの上流側に位置した場合と下流側に位
置した場合の二通りについてそれぞれ評価を行った。
Durability test: Attached to the exhaust system of an engine with a displacement of 2 liters, exhaust gas temperature 800 ° C., A / F = 14.6
After running for 50 hours under the condition of (stoichi), the above test was conducted. With respect to the exhaust gas purifying catalysts of the examples, two kinds of evaluation were performed, respectively, in the case where the Ba-supported portion was located on the upstream side of the exhaust gas and when it was located on the downstream side.

【0024】[0024]

【表1】 表1の初期データより、実施例の排気ガス浄化用触媒は
比較例2に比べて低温活性に優れ、従来の三元触媒であ
る比較例1と同等となっている。またNOx浄化率は比
較例2と同等の高い値を示している。
[Table 1] From the initial data of Table 1, the exhaust gas purifying catalyst of the example is superior to the comparative example 2 in low-temperature activity, and is equivalent to the conventional three-way catalyst of the comparative example 1. Further, the NOx purification rate shows a high value equivalent to that of Comparative Example 2.

【0025】そして耐久後においては、実施例は比較例
1と同等の低温活性を有し、比較例2に比べて低温活性
に優れている。また比較例2はNOx浄化率が大きく低
下しているのに対し、実施例は低下度合いが小さく耐久
性に優れていることが明らかである。すなわち上記評価
から明らかなように、Baを全長にわたって担持する
と、NOx吸収性能には優れているものの、耐久後には
Baによる活性サイトの被覆やシンタリングなどにより
貴金属触媒の作用が低下し、耐久性に劣る。しかしBa
を部分的に担持することにより、貴金属触媒の作用を維
持しつつ耐久後のNOxの吸収性能の低下度合いが小さ
くなり、比較例1と同等の低下度合いとなっている。
After endurance, the example has a low temperature activity equivalent to that of the comparative example 1, and is superior to the comparative example 2 in the low temperature activity. Further, it is clear that in Comparative Example 2, the NOx purification rate is greatly reduced, whereas in the Example, the degree of reduction is small and the durability is excellent. That is, as is clear from the above evaluation, when Ba is carried over the entire length, the NOx absorption performance is excellent, but after the endurance, the activity of the noble metal catalyst decreases due to the coating of active sites with Ba and sintering, etc. Inferior to. But Ba
By partially supporting, the degree of decrease in NOx absorption performance after endurance is reduced while maintaining the action of the noble metal catalyst, and the degree of decrease is equivalent to that in Comparative Example 1.

【0026】なお、Baの担持位置で上流側と下流側を
比較すると、上流側の方がNOx浄化率が高くなってい
る。また実施例2の方が実施例1よりNOx浄化率が高
い。したがって表1からは、Baの担持位置は上流側と
し、Baは軸長の25%よりも50%とする方が好まし
いということがわかる。
When comparing the upstream side and the downstream side at the Ba loading position, the NOx purification rate is higher on the upstream side. Further, the NOx purification rate of Example 2 is higher than that of Example 1. Therefore, it can be seen from Table 1 that it is preferable that the carrying position of Ba is on the upstream side and Ba is 50% rather than 25% of the axial length.

【0027】[0027]

【発明の効果】したがって本発明の排気ガス浄化用触媒
によれば、NOx吸収金属の担持によりリーン側におい
ても優れたNOxの浄化性能を有するとともに、NOx
吸収金属の分布担持により貴金属触媒の活性サイトの低
下が防止されているので、低温時においても高い触媒活
性を示し、かつ耐熱性及び耐久性に優れている。
As described above, according to the exhaust gas purifying catalyst of the present invention, the NOx absorbing metal is carried to provide excellent NOx purifying performance on the lean side as well.
Since the reduction of the active site of the noble metal catalyst is prevented by the distribution and support of the absorbing metal, it exhibits high catalytic activity even at low temperature, and is excellent in heat resistance and durability.

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

【図1】本発明の一実施例の排気ガス浄化用触媒の概略
断面図である。
FIG. 1 is a schematic sectional view of an exhaust gas purifying catalyst according to an embodiment of the present invention.

【図2】図1の要部拡大概略断面図である。FIG. 2 is an enlarged schematic cross-sectional view of a main part of FIG.

【符号の説明】[Explanation of symbols]

1:ハニカム担体基材 2:アルミ
ナコート層 3:貴金属触媒 4:NOx
吸収金属
1: Honeycomb carrier substrate 2: Alumina coat layer 3: Noble metal catalyst 4: NOx
Absorbing metal

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01J 35/04 ZAB 8017−4G 301 L 8017−4G B01D 53/36 104 A ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location B01J 35/04 ZAB 8017-4G 301 L 8017-4G B01D 53/36 104 A

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 多孔質体からなり軸方向に延びるハニカ
ム通路をもつ担体と、該担体の軸方向に均一に担持され
た貴金属触媒と、アルカリ土類金属及びアルカリ金属の
少なくとも一方からなり該担体の軸方向に濃度分布をも
って担持されたNOx吸収金属と、からなることを特徴
とする排気ガス浄化用触媒。
1. A carrier comprising a porous body having a honeycomb passage extending in the axial direction, a noble metal catalyst uniformly supported in the axial direction of the carrier, and at least one of an alkaline earth metal and an alkali metal. An exhaust gas purifying catalyst, comprising: a NOx absorption metal supported with a concentration distribution in the axial direction.
JP5281177A 1993-11-10 1993-11-10 Catalyst for purifying exhaust gas Pending JPH07132226A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5281177A JPH07132226A (en) 1993-11-10 1993-11-10 Catalyst for purifying exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5281177A JPH07132226A (en) 1993-11-10 1993-11-10 Catalyst for purifying exhaust gas

Publications (1)

Publication Number Publication Date
JPH07132226A true JPH07132226A (en) 1995-05-23

Family

ID=17635427

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5281177A Pending JPH07132226A (en) 1993-11-10 1993-11-10 Catalyst for purifying exhaust gas

Country Status (1)

Country Link
JP (1) JPH07132226A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003080081A (en) * 2001-09-12 2003-03-18 Cataler Corp Catalyst for cleaning exhaust gas
EP1726797A1 (en) 2005-05-27 2006-11-29 Ibiden Co., Ltd. Honeycomb structured body
US7169734B2 (en) 2000-11-09 2007-01-30 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst and method of producing same
JP2008291672A (en) * 2007-05-22 2008-12-04 Nissan Diesel Motor Co Ltd Exhaust emission control device for engine
JP2011078899A (en) * 2009-10-06 2011-04-21 Ngk Insulators Ltd Catalyst-supporting filter
JP2013031849A (en) * 2012-10-31 2013-02-14 Cataler Corp Exhaust gas cleaning catalyst
JP2013176774A (en) * 1999-08-23 2013-09-09 Basf Catalysts Llc Catalytic trap

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013176774A (en) * 1999-08-23 2013-09-09 Basf Catalysts Llc Catalytic trap
US7169734B2 (en) 2000-11-09 2007-01-30 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst and method of producing same
JP2003080081A (en) * 2001-09-12 2003-03-18 Cataler Corp Catalyst for cleaning exhaust gas
EP1726797A1 (en) 2005-05-27 2006-11-29 Ibiden Co., Ltd. Honeycomb structured body
JP2008291672A (en) * 2007-05-22 2008-12-04 Nissan Diesel Motor Co Ltd Exhaust emission control device for engine
JP2011078899A (en) * 2009-10-06 2011-04-21 Ngk Insulators Ltd Catalyst-supporting filter
JP2013031849A (en) * 2012-10-31 2013-02-14 Cataler Corp Exhaust gas cleaning catalyst

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