JPH0523599A - Catalyst for decontaminating exhaust gas - Google Patents

Catalyst for decontaminating exhaust gas

Info

Publication number
JPH0523599A
JPH0523599A JP3179597A JP17959791A JPH0523599A JP H0523599 A JPH0523599 A JP H0523599A JP 3179597 A JP3179597 A JP 3179597A JP 17959791 A JP17959791 A JP 17959791A JP H0523599 A JPH0523599 A JP H0523599A
Authority
JP
Japan
Prior art keywords
catalyst
barium sulfate
platinum group
group metal
supported
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.)
Granted
Application number
JP3179597A
Other languages
Japanese (ja)
Other versions
JP3299286B2 (en
Inventor
Shinya Kitaguchi
真也 北口
Shigeyoshi Taniguchi
茂良 谷口
Kazuo Tsuchiya
一雄 土谷
Tomohisa Ohata
知久 大幡
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.)
Nippon Shokubai Co Ltd
Original Assignee
Nippon Shokubai Co Ltd
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 Nippon Shokubai Co Ltd filed Critical Nippon Shokubai Co Ltd
Priority to JP17959791A priority Critical patent/JP3299286B2/en
Publication of JPH0523599A publication Critical patent/JPH0523599A/en
Application granted granted Critical
Publication of JP3299286B2 publication Critical patent/JP3299286B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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

Abstract

PURPOSE:To simultaneously remove hydrocarbon(HC), carbon monoxide(CO) and nitrogen oxide (NOx) which are harmful components discharged from an internal combustion engine such as an automobile. CONSTITUTION:A catalyst for decontaminating exhaust gas is obtained by coating a honeycomb carrier having an integral structure with the catalytic composition which incorporates barium sulfate carried with platinum group metal wherein platinum group metal is carried on barium sulfate, refractory inorganic oxide and rare earth oxide.

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
関するものである。さらに詳しくは、自動車等の内燃機
関から排出される有害成分である炭化水素(HC)、一
酸化炭素(CO)及び窒素酸化物(NOx)を同時に除
去する排気ガス浄化用触媒に関するものであり、特に高
温酸化雰囲気のような厳しい条件下で使用されても優れ
た耐久性を有し、かつ上記有害成分に対し低温での高い
浄化性能を有する排気ガス浄化用触媒に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying catalyst. More specifically, the present invention relates to an exhaust gas purifying catalyst that simultaneously removes harmful components such as hydrocarbons (HC), carbon monoxide (CO), and nitrogen oxides (NOx) emitted from internal combustion engines of automobiles, In particular, the present invention relates to an exhaust gas purifying catalyst that has excellent durability even when used under severe conditions such as a high temperature oxidizing atmosphere, and that has high purification performance at low temperatures against the above harmful components.

【0002】[0002]

【従来の技術】従来、自動車等の内燃機関から排出され
る排気ガス浄化用触媒において白金族金属は、活性アル
ミナ等の高表面積の耐火性無機酸化物上に高分散に担持
されていたため、初期活性は高いものの高温酸化雰囲気
のような厳しい条件にさらされると白金族金属が粒子成
長したり、アルミナ等の担体物質やセリア等の助触媒成
分と好ましくない相互作用により大きな性能低下が見ら
れた。特に白金族金属の担体物質として活性アルミナを
使用する場合は900℃以上の高温においてα−アルミ
ナへの相転移があり、触媒性能の低下は避けられないも
のであった。
2. Description of the Related Art Conventionally, in a catalyst for purifying exhaust gas discharged from an internal combustion engine of an automobile or the like, a platinum group metal is supported in a high dispersion on a high surface area refractory inorganic oxide such as activated alumina. Although the activity is high, platinum group metal particles grow when exposed to severe conditions such as high temperature oxidizing atmosphere, and a large decrease in performance was observed due to unfavorable interaction with carrier materials such as alumina and cocatalyst components such as ceria. . In particular, when activated alumina is used as the platinum group metal carrier material, there is a phase transition to α-alumina at a high temperature of 900 ° C. or higher, and the deterioration of the catalytic performance is unavoidable.

【0003】上記問題点に対して例えば米国特許423
3189号や米国特許4172047号において白金族
金属と相互作用しない担体物質としてジルコニアあるい
はα−アルミナの使用が提案されているが白金族金属の
粒子成長を抑制するものではなく十分な性能は得られて
いない。さらに白金族金属を活性アルミナに担持した場
合は酸性のスラリー作成時において担体物質である活性
アルミナの溶出が確認されており、これが触媒性能低下
の一因となっている。
For the above problems, for example, US Pat. No. 423
3189 and U.S. Pat. No. 4,172,047 propose the use of zirconia or α-alumina as a carrier material that does not interact with the platinum group metal, but does not suppress the particle growth of the platinum group metal and has sufficient performance. Absent. Further, when a platinum group metal is supported on activated alumina, it has been confirmed that activated alumina, which is a carrier substance, elutes when an acidic slurry is prepared, which is one of the causes of deterioration of catalytic performance.

【0004】一方、特開昭61−234931号や特開
昭62−149343においては白金族金属の担体物質
である活性アルミナにLa,Nd等の希土類元素やB
a,Sr等のアルカリ土類金属元素を添加してα−アル
ミナへの相転移を抑制する方法が開示されているがその
効果は十分ではなく、逆に上記添加物は白金族金属や助
触媒である酸化セリウムに悪影響をもたらして触媒性能
低下を起こしたり、スラリー性状が悪化するという問題
点があった。
On the other hand, in JP-A-61-234931 and JP-A-62-149343, rare earth elements such as La and Nd and B are added to activated alumina which is a platinum group metal carrier material.
Although a method of suppressing the phase transition to α-alumina by adding an alkaline earth metal element such as a or Sr is disclosed, the effect is not sufficient, and conversely, the above-mentioned additive is a platinum group metal or a cocatalyst. However, there is a problem that the cerium oxide, which is the above, is adversely affected and the catalyst performance is deteriorated, and the slurry properties are deteriorated.

【0005】[0005]

【発明が解決しようとする課題】従って本発明の目的は
白金族金属を有効的に利用し、かつエンジン排ガス等の
高温条件下で使用されても触媒の性能の大きな低下がな
い新規な排気ガス浄化用触媒を提供することにある。
Therefore, an object of the present invention is to provide a novel exhaust gas that effectively utilizes platinum group metals and does not cause a significant deterioration in catalyst performance even when used under high temperature conditions such as engine exhaust gas. It is to provide a purification catalyst.

【0006】[0006]

【課題を解決するための手段】本発明者等は鋭意研究の
結果、白金族金属を硫酸バリウム上に担持せしめた白金
族金属担持硫酸バリウムを含有する触媒は900℃以
上、特に1000℃を越える高温下で使用されても優れ
た触媒性能を維持することを見出し本発明を完成するに
至った。
Means for Solving the Problems As a result of earnest studies by the present inventors, a catalyst containing platinum group metal-supported barium sulfate in which a platinum group metal is supported on barium sulfate has a temperature of 900 ° C. or higher, particularly 1000 ° C. or higher. The inventors have found that they maintain excellent catalyst performance even when used at high temperatures, and have completed the present invention.

【0007】上記目的は本発明に従い硫酸バリウム上に
担持された白金族金属と活性アルミナ等の耐火性無機酸
化物及びセリウム酸化物等の希土類酸化物を含有してな
る触媒組成物を一体構造を有するハニカム担体に被覆せ
しめてなることを特徴とする排気ガス浄化用触媒によっ
て達成される。
According to the present invention, there is provided an integrated structure of a catalyst composition comprising a platinum group metal supported on barium sulfate, a refractory inorganic oxide such as activated alumina, and a rare earth oxide such as cerium oxide. The present invention is achieved by an exhaust gas purifying catalyst, which is obtained by coating the honeycomb carrier of the present invention.

【0008】使用される硫酸バリウムは特に限定され
ず、市販品、あるいはバリウム塩水溶液に希硫酸を加え
て得られる白色沈澱を濾過洗浄する方法等によって得ら
れるものであってもよい。硫酸バリウムの比表面積は通
常0.1〜10m2/g程度であり1200℃以上の高
温まで安定であることが知られている。この硫酸バリウ
ムは排気ガス浄化用触媒1リットル当たり1〜50g使
用することができる。
The barium sulfate used is not particularly limited, and may be a commercially available product, or a product obtained by filtering and washing a white precipitate obtained by adding dilute sulfuric acid to an aqueous barium salt solution. It is known that the specific surface area of barium sulfate is usually about 0.1 to 10 m 2 / g and is stable up to 1200 ° C. or higher. This barium sulfate can be used in an amount of 1 to 50 g per liter of exhaust gas purifying catalyst.

【0009】本発明にかかわる白金族金属は白金、パラ
ジウム又はロジウム等の白金族金属を単独あるいは組合
せて使用され、排気ガス浄化用触媒1リットル当たり
0.1〜5.0g使用することができる。
As the platinum group metal according to the present invention, platinum group metals such as platinum, palladium and rhodium are used alone or in combination, and 0.1 to 5.0 g can be used per 1 liter of exhaust gas purifying catalyst.

【0010】これら白金族金属は上記硫酸バリウム上に
通常の方法により担持せしめることが可能である。例え
ば含浸法においては、白金族金属の塩溶液を硫酸バリウ
ムに含浸しその後乾燥、焼成することによって白金族金
属担持硫酸バリウムが得られる。白金族金属の硫酸バリ
ウムへの担持濃度は0.5〜30重量%好ましくは1〜
20重量%の範囲で担持される。また2種類以上の白金
族金属を触媒組成物に含有させる場合においては全量を
同じ硫酸バリウムに担持する方法、別々に硫酸バリウム
に担持する方法、又は一部を硫酸バリウムに担持し残り
を耐火性無機酸化物または希土類酸化物に担持する方法
をとることができる。
These platinum group metals can be supported on the above barium sulfate by an ordinary method. For example, in the impregnation method, barium sulfate supporting platinum group metal is obtained by impregnating barium sulfate with a salt solution of a platinum group metal, followed by drying and firing. The supported concentration of the platinum group metal on barium sulfate is 0.5 to 30% by weight, preferably 1 to
It is supported in the range of 20% by weight. When two or more platinum group metals are contained in the catalyst composition, all of them are supported on the same barium sulfate, separately supported on barium sulfate, or partially supported on barium sulfate and the rest is refractory. A method of loading on an inorganic oxide or a rare earth oxide can be used.

【0011】耐火性無機酸化物はアルミナ、シリカ、チ
タニア、若しくはジルコニアの各々の酸化物、またはこ
れらの複合酸化物若しくは混合物が使用することがで
き、好ましくは活性アルミナである。この耐火性無機酸
化物は排気ガス浄化用触媒1リットル当たり30〜30
0g使用することができる。
The refractory inorganic oxide may be an oxide of alumina, silica, titania, or zirconia, or a complex oxide or mixture thereof, preferably activated alumina. This refractory inorganic oxide is 30 to 30 per liter of exhaust gas purifying catalyst.
0 g can be used.

【0012】次に希土類酸化物の触媒組成物への添加方
法としては、酸化物又は炭酸化物、水酸化物等の化合物
で焼成時若しくは使用時に酸化物の形態になる前駆体化
合物を触媒組成物に含有させる方法、又は前記の前駆体
化合物を活性アルミナ等の耐火性無機酸化物上に担持す
る方法があり、この場合は耐火性無機酸化物に対して
0.1〜50重量%の範囲で担持することが好ましい。
また希土類酸化物としてはセリウム、ランタン、ネオジ
ム等の各酸化物が挙げられるが、特にセリウム酸化物の
使用が好ましく、排気ガス浄化用触媒1リットル当たり
5〜100g使用することができる。
Next, as a method of adding the rare earth oxide to the catalyst composition, a precursor compound which is in the form of an oxide upon firing or in use, is prepared from a compound such as an oxide, a carbonate or a hydroxide. Or a method of supporting the precursor compound on a refractory inorganic oxide such as activated alumina. In this case, in the range of 0.1 to 50% by weight with respect to the refractory inorganic oxide. It is preferable to carry.
Examples of the rare earth oxide include cerium, lanthanum, neodymium, and the like, but it is particularly preferable to use cerium oxide, and 5 to 100 g can be used per liter of exhaust gas purifying catalyst.

【0013】このようにして得られた白金族金属担持硫
酸バリウム,耐火性無機酸化物および希土類酸化物を含
有してなる触媒組成物は通常の方法によりボールミル等
を用いて水性スラリーとしモノリス構造を有するハニカ
ム担体に被覆せしめて、その後乾燥し必要により焼成し
て完成触媒とする。
The thus obtained catalyst composition containing barium sulfate supporting platinum group metal, refractory inorganic oxide and rare earth oxide is made into an aqueous slurry by a usual method using a ball mill or the like to form a monolith structure. The resulting honeycomb carrier is coated with it, then dried and fired if necessary to obtain a finished catalyst.

【0014】本発明で使用されるモノリス担体としては
コージェライト、ムライト等のセラミックモノリス担体
及びステンレス又はFe−Cr−Al合金等のメタルモ
ノリス担体が挙げられる。
Examples of the monolith carrier used in the present invention include ceramic monolith carriers such as cordierite and mullite, and metal monolith carriers such as stainless steel and Fe—Cr—Al alloy.

【0015】[0015]

【効果】本発明の排気ガス浄化用触媒においては白金族
金属は硫酸バリウムに担持されていることを特徴とす
る。硫酸バリウムは水不溶性であり、スラリー調製時に
おいても溶出がほとんどなく、かつ硫酸バリウムは高温
にさらされてもほとんど変化しない熱的に安定な物質で
あるため、白金族金属は十分に固定される。
[Effect] The catalyst for purifying exhaust gas of the present invention is characterized in that the platinum group metal is supported on barium sulfate. Barium sulphate is insoluble in water, hardly elutes during slurry preparation, and barium sulphate is a thermally stable substance that hardly changes even when exposed to high temperatures, so the platinum group metal is sufficiently fixed. .

【0016】また詳細なことは不明であるが硫酸バニウ
ムは白金族金属と好ましい相互作用を有しており、例え
ば白金族金属の粒子成長を抑制する効果があると考えら
れる。この結果、900℃以上の高温条件にさらされて
も触媒性能の大きな低下がなく白金族金属を有効的に利
用することができる。
Although the details are not clear, it is considered that vanium sulfate has a preferable interaction with the platinum group metal and has an effect of suppressing particle growth of the platinum group metal, for example. As a result, the platinum group metal can be effectively used without significant deterioration in catalytic performance even when exposed to high temperature conditions of 900 ° C. or higher.

【0017】以下実施例にて具体的に説明するが、本発
明の趣旨に反しない限り、これら実施例に限定されるこ
とはない。
Specific examples will be described below, but the examples are not limited to these examples as long as the object of the present invention is not impaired.

【0018】[0018]

【実施例1】白金2.0gを含有するジニトロジアミノ
白金及びロジウム0.4gを含有する硝酸ロジウムの混
合水溶液を比表面積5m2/gの硫酸バリウム20gに
含浸し150℃にて乾燥した後500℃1時間焼成して
白金族金属担持硫酸バリウムを調製した。このようにし
て得られた白金族金属担持硫酸バリウムと市販の酸化セ
リウム80gおよび比表面積150m2/gの活性アル
ミナ200gをボールミルにて15時間粉砕して得られ
た水性スラリーにコージェライト製モノリス担体(40
0セル/平方インチ)を浸漬し、余剰スラリーを圧縮空
気にて吹き飛ばした後150℃にて2時間乾燥し完成触
媒(1)を得た。
Example 1 20 g of barium sulfate having a specific surface area of 5 m 2 / g was impregnated with a mixed aqueous solution of dinitrodiaminoplatinum containing 2.0 g of platinum and rhodium nitrate containing 0.4 g of rhodium and dried at 150 ° C., and then 500 The barium sulfate carrying platinum group metal was prepared by firing at ℃ for 1 hour. A monolithic carrier made of cordierite was obtained by pulverizing the barium sulfate supporting platinum group metal thus obtained, 80 g of commercially available cerium oxide, and 200 g of activated alumina having a specific surface area of 150 m 2 / g in a ball mill for 15 hours. (40
0 cell / square inch) was dipped, the excess slurry was blown off with compressed air, and then dried at 150 ° C. for 2 hours to obtain a finished catalyst (1).

【0019】[0019]

【比較例1】白金2.0gを含有するジニトロジアミノ
白金及びロジウム0.4gを含有する硝酸ロジウムの混
合水溶液を活性アルミナ200gに含浸し150℃にて
乾燥した後500℃1時間焼成して白金族金属担持アル
ミナを調製した。このようにして得られた白金族金属担
持アルミナと市販の酸化セリウム80gおよび硫酸バリ
ウム20gをボールミルにて粉砕し、水性スラリーを得
た。以下実施例1と同様にして比較触媒(A)を得た。
Comparative Example 1 Platinum was prepared by impregnating 200 g of activated alumina with a mixed aqueous solution of dinitrodiamino platinum containing 2.0 g of platinum and rhodium nitrate containing 0.4 g of rhodium, drying at 150 ° C., and then firing at 500 ° C. for 1 hour. A group metal-supported alumina was prepared. The platinum group metal-supported alumina thus obtained, 80 g of commercially available cerium oxide, and 20 g of barium sulfate were pulverized with a ball mill to obtain an aqueous slurry. Thereafter, a comparative catalyst (A) was obtained in the same manner as in Example 1.

【0020】[0020]

【比較例2】比較例1において硫酸バリウムの代りに硝
酸バリウム22gを使用した以外は比較例1と同様にし
て比較触媒(B)を得た。
Comparative Example 2 A comparative catalyst (B) was obtained in the same manner as in Comparative Example 1 except that 22 g of barium nitrate was used instead of barium sulfate.

【0021】[0021]

【実施例2】白金2.0gを含有するジニトロジアミノ
白金及びロジウム0.4gを含有する硝酸ロジウムの混
合水溶液を硫酸バリウム40gに含浸し150℃にて乾
燥した後500℃1時間焼成して白金族金属担持硫酸バ
リウムを調製した。次に硝酸セリウム水溶液(25重量
%)320gを活性アルミナ180gに含浸し150℃
にて乾燥した後500℃1時間焼成して酸化セリウム担
持アルミナを調製した。このようにして得られた2種の
粉体をボールミルにて粉砕し、水性スラリーを得た。以
下実施例1と同様にして完成触媒(2)を得た。
Example 2 40 g of barium sulfate was impregnated with a mixed aqueous solution of dinitrodiaminoplatinum containing 2.0 g of platinum and rhodium nitrate containing 0.4 g of rhodium, dried at 150 ° C., and then calcined at 500 ° C. for 1 hour to obtain platinum. A group metal-supported barium sulfate was prepared. Next, 320 g of a cerium nitrate aqueous solution (25% by weight) was impregnated into 180 g of activated alumina to obtain 150 °
After drying in, the mixture was baked at 500 ° C. for 1 hour to prepare cerium oxide-supported alumina. The two types of powder thus obtained were crushed with a ball mill to obtain an aqueous slurry. Thereafter, a completed catalyst (2) was obtained in the same manner as in Example 1.

【0022】[0022]

【実施例3】実施例2において白金2.0gおよびロジ
ウム0.4gをそれぞれ別々の硫酸バリウム20gに担
持した以外は実施例2と同様にして完成触媒(3)を得
た。
Example 3 A finished catalyst (3) was obtained in the same manner as in Example 2 except that 2.0 g of platinum and 0.4 g of rhodium were respectively supported on 20 g of barium sulfate.

【0023】[0023]

【比較例3】実施例2において硫酸バリウムの代りに比
表面積3m2/gのα−アルミナ40gを使用した以外
は実施例2と同様にして比較触媒(C)を得た。
Comparative Example 3 A comparative catalyst (C) was obtained in the same manner as in Example 2 except that 40 g of α-alumina having a specific surface area of 3 m 2 / g was used in place of barium sulfate.

【0024】[0024]

【実施例4】パラジウム2.0gを含有する硝酸パラジ
ウム及びロジウム0.4gを含有する硝酸ロジウムの混
合水溶液を比表面積5m2/gの硫酸バリウム30gに
含浸し150℃で乾燥し、次いで500℃で1時間焼成
して白金族金属担持硫酸バリウムを調製した。この白金
族金属担持硫酸バリウムと市販の酸化セリウム80g及
び比表面積150m2/gの活性アルミナ190gをボ
ールミルで15時間湿式粉砕し、水性スラリーを得た。
以下実施例1と同様にして完成触媒(4)を得た。
Example 4 30 g of barium sulfate having a specific surface area of 5 m 2 / g was impregnated with a mixed aqueous solution of palladium nitrate containing 2.0 g of palladium and rhodium nitrate containing 0.4 g of rhodium, dried at 150 ° C., and then 500 ° C. Then, it was baked for 1 hour to prepare barium sulfate carrying platinum group metal. The platinum group metal-supported barium sulfate, 80 g of commercially available cerium oxide, and 190 g of activated alumina having a specific surface area of 150 m 2 / g were wet-ground for 15 hours with a ball mill to obtain an aqueous slurry.
Thereafter, a completed catalyst (4) was obtained in the same manner as in Example 1.

【0025】[0025]

【比較例4】比表面積150m2/gの活性アルミナを
ボールミルで湿式粉砕して水性スラリーを調製し、モノ
リス担体に活性アルミナをコートしたのち、モノリス担
体を硝酸セリウム水溶液に浸漬し乾燥後、500℃で1
時間焼成してセリウムを担持した後、次いで硝酸パラジ
ウム及び硝酸ロジウムの水溶液に浸漬し、乾燥後、50
0℃で1時間焼成して白金族金属を担持した。このよう
にして得られたモノリス担体を酢酸バリウム水溶液に浸
漬し、乾燥後、500℃で1時間焼成して比較触媒
(D)を得た。
Comparative Example 4 Activated alumina having a specific surface area of 150 m 2 / g was wet pulverized with a ball mill to prepare an aqueous slurry, the activated alumina was coated on the monolith carrier, and the monolith carrier was immersed in an aqueous cerium nitrate solution and dried. 1 at ℃
After calcination for a period of time to support cerium, it is then immersed in an aqueous solution of palladium nitrate and rhodium nitrate and dried, then 50
The platinum group metal was supported by firing at 0 ° C. for 1 hour. The monolithic carrier thus obtained was immersed in an aqueous barium acetate solution, dried and then calcined at 500 ° C. for 1 hour to obtain a comparative catalyst (D).

【0026】[0026]

【試験例】実施例より得られた触媒1〜4及び比較例よ
り得られた触媒A〜Dについてエンジン耐久走行後の触
媒性能を試験した。耐久エンジンは電子制御エンジン
(8気筒4400cc)を使用し定常運転60秒、減速
6秒(減速時には燃料がカットされ触媒は高温酸化雰囲
気にさらされる)というモード運転を実施し定常運転で
触媒温度が1000℃となる条件で50時間触媒をエー
ジングした。触媒の評価は1800cc電子制御エンジ
ンを用いて行ない触媒入口温度450℃におけるCO、
HCおよびNOxの浄化率を測定した結果を表1に示し
た。
Test Example Catalysts 1 to 4 obtained from the examples and catalysts A to D obtained from the comparative examples were tested for catalyst performance after engine running. The endurance engine uses an electronically controlled engine (8 cylinders 4400cc) and carries out a mode operation of 60 seconds of steady operation and 6 seconds of deceleration (fuel is cut and the catalyst is exposed to a high-temperature oxidizing atmosphere during deceleration), and the catalyst temperature is increased in steady operation. The catalyst was aged for 50 hours under the condition of 1000 ° C. The catalyst was evaluated using an 1800 cc electronically controlled engine, CO at a catalyst inlet temperature of 450 ° C.,
The results of measuring the purification rates of HC and NOx are shown in Table 1.

【0027】[0027]

【表1】 [Table 1]

【0028】表1の結果より本発明に開示する排気ガス
浄化用触媒は高温酸化雰囲気のような厳しい条件下で使
用されても性能の低下が少ない優れた触媒であることは
明らかである。
From the results shown in Table 1, it is clear that the exhaust gas purifying catalyst disclosed in the present invention is an excellent catalyst with little deterioration in performance even when used under severe conditions such as a high temperature oxidizing atmosphere.

フロントページの続き (72)発明者 大幡 知久 兵庫県姫路市網干区興浜字西沖992番地の 1 株式会社日本触媒触媒研究所内Continued front page    (72) Inventor Tomohisa Ohata             Hyogo prefecture Himeji city             1 Inside Japan Catalyst Research Institute

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】白金族金属を硫酸バリウム上に担持せしめ
てなる白金族金属担持硫酸バリウム、耐火性無機酸化物
及び希土類酸化物を含有してなる触媒組成物を一体構造
を有するハニカム担体に被覆せしめてなることを特徴と
する排気ガス浄化用触媒。
1. A honeycomb carrier having an integral structure is coated with a catalyst composition containing a platinum group metal-supported barium sulfate in which a platinum group metal is supported on barium sulfate, a refractory inorganic oxide and a rare earth oxide. An exhaust gas purifying catalyst characterized by being made at the most.
【請求項2】白金、パラジウムおよびロジウムよりなる
群から選択される少なくとも一種の白金族金属を硫酸バ
リウムに対して0.5〜30重量%の担持濃度となるよ
うに硫酸バリウム上に担持する請求項1記載の触媒。
2. At least one platinum group metal selected from the group consisting of platinum, palladium and rhodium is supported on barium sulfate so as to have a supported concentration of 0.5 to 30% by weight with respect to barium sulfate. The catalyst according to item 1.
JP17959791A 1991-07-19 1991-07-19 Exhaust gas purification catalyst Expired - Lifetime JP3299286B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP17959791A JP3299286B2 (en) 1991-07-19 1991-07-19 Exhaust gas purification catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP17959791A JP3299286B2 (en) 1991-07-19 1991-07-19 Exhaust gas purification catalyst

Publications (2)

Publication Number Publication Date
JPH0523599A true JPH0523599A (en) 1993-02-02
JP3299286B2 JP3299286B2 (en) 2002-07-08

Family

ID=16068520

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP3299286B2 (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0848983A1 (en) * 1996-12-20 1998-06-24 Ngk Insulators, Ltd. Catalyst for exhaust gas purification and system for exhaust gas purification
JP2001062295A (en) * 1999-08-30 2001-03-13 Daihatsu Motor Co Ltd Exhaust gas cleaning catalyst
JP2001070792A (en) * 1999-09-03 2001-03-21 Daihatsu Motor Co Ltd Catalyst for cleaning exhaust gas
JP2002011350A (en) * 1999-05-24 2002-01-15 Daihatsu Motor Co Ltd Exhaust gas cleaning catalyst
JP2007216200A (en) * 2006-01-20 2007-08-30 Matsushita Electric Ind Co Ltd Exhaust gas purifying catalyst
JP2012236193A (en) * 1993-04-28 2012-12-06 Nippon Shokubai Co Ltd Method of removing nitrogen oxides in exhaust gas

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012236193A (en) * 1993-04-28 2012-12-06 Nippon Shokubai Co Ltd Method of removing nitrogen oxides in exhaust gas
EP0848983A1 (en) * 1996-12-20 1998-06-24 Ngk Insulators, Ltd. Catalyst for exhaust gas purification and system for exhaust gas purification
US6500392B2 (en) 1996-12-20 2002-12-31 Ngk Insulators, Ltd. Catalyst for exhaust gas purification and system for exhaust gas purification
JP2002011350A (en) * 1999-05-24 2002-01-15 Daihatsu Motor Co Ltd Exhaust gas cleaning catalyst
JP2001062295A (en) * 1999-08-30 2001-03-13 Daihatsu Motor Co Ltd Exhaust gas cleaning catalyst
JP2001070792A (en) * 1999-09-03 2001-03-21 Daihatsu Motor Co Ltd Catalyst for cleaning exhaust gas
JP2007216200A (en) * 2006-01-20 2007-08-30 Matsushita Electric Ind Co Ltd Exhaust gas purifying catalyst

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