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JPH06378A - Catalyst for purification of exhaust gas - Google Patents

Catalyst for purification of exhaust gas

Info

Publication number
JPH06378A
JPH06378A JP4159416A JP15941692A JPH06378A JP H06378 A JPH06378 A JP H06378A JP 4159416 A JP4159416 A JP 4159416A JP 15941692 A JP15941692 A JP 15941692A JP H06378 A JPH06378 A JP H06378A
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
purification
platinum
oxide
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
JP4159416A
Other languages
Japanese (ja)
Inventor
Toru Sekiba
徹 関場
Akihide Okada
晃英 岡田
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.)
Nissan Motor Co Ltd
Original Assignee
Nissan Motor 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 Nissan Motor Co Ltd filed Critical Nissan Motor Co Ltd
Priority to JP4159416A priority Critical patent/JPH06378A/en
Publication of JPH06378A publication Critical patent/JPH06378A/en
Pending legal-status Critical Current

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

Abstract

PURPOSE:To obtain a catalyst for purification of exhaust gas having such performance that exhaust gas which varies considerably in compsn. from the internal- combustion engine of an automobile, etc., can be purified at a high rate of purification. CONSTITUTION:This catalyst for purification of exhaust gas is a monolithic catalyst with a catalytic component supported layer formed by supporting at least one of Pt and Pd and the oxide of at least one kind of metal selected from among K, Cs, Sr and Ba as catalytic components on activated alumina and cerium 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】この発明は、自動車などの内燃機
関から排出される排ガス中の炭化水素(HC)、一酸化
炭素(CO)、および窒素酸化物(NOx )を浄化す
る、排ガス浄化用触媒に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention purifies exhaust gas, which purifies hydrocarbons (HC), carbon monoxide (CO), and nitrogen oxides (NO x ) in exhaust gas discharged from internal combustion engines such as automobiles. For catalysts.

【0002】[0002]

【従来の技術】従来の排ガス浄化用触媒としては、例え
ば特公昭58−20307 号公報に開示されている白金、ロジ
ウムおよびセリウムから成る組成物を耐火性担体に担持
させた排出ガス浄化用触媒のように、アルミナや酸化セ
リウムなどに白金、パラジウムおよびロジウムなどの白
金族元素を担持させ、これをモノリス担体にコーティン
グした構造のものが使われている。
2. Description of the Related Art As a conventional exhaust gas purifying catalyst, for example, an exhaust gas purifying catalyst in which a composition consisting of platinum, rhodium and cerium disclosed in Japanese Patent Publication No. 58-20307 is supported on a refractory carrier is disclosed. As described above, a structure in which a platinum group element such as platinum, palladium and rhodium is supported on alumina, cerium oxide or the like and the monolith carrier is coated with the platinum group element is used.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、還元性
から酸化性まで幅広く組成が変動する排ガスを処理する
排ガス浄化用触媒において、特に炭化水素濃度が高く酸
素濃度が十分でない条件では炭化水素の強い吸着被毒が
触媒活性金属に対して起こることにより浄化反応が阻害
され、有害成分の浄化率が低くなってしまうという問題
点があった。
However, in an exhaust gas purifying catalyst for treating exhaust gas whose composition varies widely from reducing properties to oxidizing properties, strong adsorption of hydrocarbons is observed especially under conditions of high hydrocarbon concentration and insufficient oxygen concentration. When the catalytically active metal is poisoned, the purification reaction is hindered, and the purification rate of harmful components becomes low.

【0004】[0004]

【課題を解決するための手段】この発明は、このような
従来の問題点に着目してなされたもので、白金族元素、
活性アルミナ、酸化セリウム等、従来から触媒成分とし
て使われるものに加えて、カリウム化合物、セシウム化
合物、ストロンチウム化合物、バリウム化合物のうち少
なくとも1種類を組み合わせることにより、炭化水素濃
度が高く酸素濃度が低い排気ガスに対しても高い浄化率
を達成することができることを見出し、この発明を達成
するに至った。
SUMMARY OF THE INVENTION The present invention has been made by paying attention to such conventional problems as described above.
Exhaust with high hydrocarbon concentration and low oxygen concentration by combining at least one of potassium compounds, cesium compounds, strontium compounds, and barium compounds in addition to those conventionally used as catalyst components such as activated alumina and cerium oxide. It has been found that a high purification rate can be achieved even for gas, and the present invention has been achieved.

【0005】従ってこの発明の排ガス浄化用触媒は、触
媒成分担持層を有する一体構造型触媒において、触媒成
分担持層が活性アルミナと酸化セリウムに触媒成分とし
て白金とパラジウムのうち少なくとも1種と、カリウ
ム、セシウム、ストロンチウムおよびバリウムから成る
群から選ばれた少なくとも1種の金属の酸化物が担持さ
れて成ることを特徴とする。
Therefore, the exhaust gas purifying catalyst of the present invention is an integral structure type catalyst having a catalyst component supporting layer, wherein the catalyst component supporting layer comprises activated alumina and cerium oxide, and at least one of platinum and palladium as catalyst components and potassium. , Cesium, strontium, and barium, and at least one metal selected from the group consisting of oxides is carried.

【0006】この発明の触媒において、白金(Pt)お
よびパラジウム(Pd)の担持量は、それぞれ完成触媒
1リットル当り0.1 〜10gであるのが好ましい。またカ
リウム化合物、セリウム化合物、ストロンチウム化合物
およびバリウム化合物の担持量は、それぞれ完成触媒1
リットル当り、酸化物に換算して1〜30gであるのが好
ましく、1g/L未満では、炭化水素濃度が高く酸素濃
度が低い排気ガスに対しても高い浄化率を達成するとい
う所期の効果が得られず、一方30g/Lより多くしても
効果が上ることはない。
In the catalyst of the present invention, the amounts of platinum (Pt) and palladium (Pd) supported are preferably 0.1 to 10 g per liter of the finished catalyst. In addition, the supported amounts of the potassium compound, the cerium compound, the strontium compound, and the barium compound are respectively those of the finished catalyst 1
It is preferably 1 to 30 g in terms of oxide per liter, and if it is less than 1 g / L, the desired effect is to achieve a high purification rate even for exhaust gas with high hydrocarbon concentration and low oxygen concentration. However, even if the amount is more than 30 g / L, the effect is not improved.

【0007】次にこの発明の触媒の製造方法を説明す
る。まず活性アルミナと酸化セリウムにカリウム、セシ
ウム、ストロンチウムおよびバリウムから成る群から選
ばれた少なくとも1種の化合物を含む水溶液を含浸す
る。用いる化合物は硝酸塩、塩化物、炭酸塩、酢酸塩、
水酸化物など水溶性のものであればよい。これを乾燥し
た後例えば500 ℃で1時間、空気中で焼成し、活性アル
ミナに対してこれら元素を1〜30重量%含む粉末(イ)
を得る。同時に活性アルミナにはジルコニウム、セリウ
ム、ランタンおよびネオジウムよりなる群から選ばれた
少なくとも1種が添加されていてもよい。
Next, a method for producing the catalyst of the present invention will be described. First, activated alumina and cerium oxide are impregnated with an aqueous solution containing at least one compound selected from the group consisting of potassium, cesium, strontium and barium. The compounds used are nitrates, chlorides, carbonates, acetates,
Any water-soluble substance such as hydroxide may be used. After this is dried, it is calcined in air at 500 ° C. for 1 hour, for example, and powder (a) containing 1 to 30% by weight of these elements relative to activated alumina
To get At the same time, at least one selected from the group consisting of zirconium, cerium, lanthanum and neodymium may be added to the activated alumina.

【0008】次いでこの粉末(イ)に白金とパラジウム
のうち少なくとも1種の白金族元素の塩を含む水溶液を
含浸し、乾燥した後、例えば400 ℃で1時間、空気中で
焼成し、完成触媒に対し白金族元素を0.1 〜10重量%含
む粉末(ロ)を得る。上記粉末(ロ)とアルミナゾル、
必要に応じて酸化セリウムなどを混合・粉砕して、スラ
リーとし、触媒担体、例えばモノリス担体基材に付着さ
せ、例えば400 〜650℃の温度で焼成し、排気ガス浄化
用触媒を得る。成分の異なるスラリー数種を調製して担
体基材に層状に付着させてもよい。また、更に性能を向
上させるためにロジウムを含む触媒層を追加して設けて
もよい。
Next, this powder (a) is impregnated with an aqueous solution containing a salt of at least one platinum group element of platinum and palladium, dried and then calcined in the air at 400 ° C. for 1 hour, for example, to obtain a finished catalyst. On the other hand, powder (b) containing 0.1 to 10% by weight of platinum group element is obtained. The above powder (b) and alumina sol,
If necessary, cerium oxide or the like is mixed and pulverized to form a slurry, which is attached to a catalyst carrier, for example, a monolith carrier substrate, and calcined at a temperature of 400 to 650 ° C. to obtain an exhaust gas purifying catalyst. It is also possible to prepare several kinds of slurries having different components and attach them in layers to the carrier substrate. Further, in order to further improve the performance, a catalyst layer containing rhodium may be additionally provided.

【0009】[0009]

【作用】排気ガス浄化用触媒は酸化性から還元性まで幅
広く組成が変化する排気ガスを処理しなければならない
が、炭化水素濃度が高く、酸素濃度が低いような強い還
元性のガスでは浄化率が低下しやすい。これは炭化水素
の強い吸着が起こり、活性金属表面が炭化水素種で覆わ
れることにより、酸素など他のガスが吸着できず反応が
進行しないためと考えられる。本発明者らは鋭意研究の
結果カリウム化合物、セシウム化合物、ストロンチウム
化合物、バリウム化合物の添加が、この還元性ガス雰囲
気における浄化率を向上するために有効であることを見
いだし、本発明を完成させた。
[Function] Exhaust gas purification catalysts must treat exhaust gas whose composition varies widely from oxidizing to reducing, but the purification rate for strongly reducing gases with high hydrocarbon concentration and low oxygen concentration Is easy to decrease. This is probably because strong adsorption of hydrocarbons occurs and the surface of the active metal is covered with hydrocarbon species, so that other gases such as oxygen cannot be adsorbed and the reaction does not proceed. As a result of intensive research, the present inventors have found that addition of a potassium compound, a cesium compound, a strontium compound, and a barium compound is effective for improving the purification rate in this reducing gas atmosphere, and completed the present invention. .

【0010】[0010]

【実施例】この発明を次の実施例、比較例および試験例
により説明する。 実施例1 活性アルミナに硝酸セリウム水溶液と硝酸カリウム水溶
液を含浸し、乾燥した後500 ℃で1時間焼成した。この
ときのセリウムの担持濃度は7重量%、カリウムの担持
濃度は5%(完全触媒1L当り酸化カリウム8.4 g)。
こうして得られた粉末に硝酸パラジウム水溶液を含浸
し、乾燥した後400 ℃で1時間焼成して、Pd担持活性
アルミナ粉末を得た。Pdの担持濃度は1.00重量%。こ
の粉末700g、酸化セリウム粉末300 g、アルミナゾル1
000gをボールミルで混合、粉砕して得られたスラリー
をモノリス担体基材(1.3 L,400 セル)に付着させ焼
成(400 ℃、1時間)した。この時の付着量は200 g/
Lに設定した。このようにして触媒(A)を得た。触媒
(A)におけるPd量は1.8 g/個になっていた。
The present invention will be described with reference to the following examples, comparative examples and test examples. Example 1 Activated alumina was impregnated with an aqueous cerium nitrate solution and an aqueous potassium nitrate solution, dried, and then calcined at 500 ° C. for 1 hour. At this time, the supported concentration of cerium was 7% by weight, and the supported concentration of potassium was 5% (8.4 g of potassium oxide per liter of complete catalyst).
The powder thus obtained was impregnated with an aqueous palladium nitrate solution, dried and then calcined at 400 ° C. for 1 hour to obtain a Pd-supported activated alumina powder. The supported concentration of Pd is 1.00% by weight. This powder 700g, cerium oxide powder 300g, alumina sol 1
A slurry obtained by mixing and crushing 000 g with a ball mill was attached to a monolith carrier substrate (1.3 L, 400 cells) and baked (400 ° C., 1 hour). The adhesion amount at this time is 200 g /
Set to L. Thus, the catalyst (A) was obtained. The amount of Pd in the catalyst (A) was 1.8 g / piece.

【0011】実施例2 実施例1において硝酸カリウムを硝酸セシウムに変えセ
シウムの担持濃度を5%(完全触媒1L当り酸化セシウ
ム7.4 g)にした以外同様にして触媒(B)を得た。
Example 2 A catalyst (B) was obtained in the same manner as in Example 1 except that potassium nitrate was changed to cesium nitrate and the supported concentration of cesium was changed to 5% (7.4 g of cesium oxide per 1 L of the complete catalyst).

【0012】実施例3 実施例1において硝酸カリウムを酢酸ストロンチウムに
変え、ストロンチウムの担持濃度を5%(完全触媒1L
当り酸化ストロンチウム8.3 g)にした以外同様にして
触媒(C)を得た。
Example 3 In Example 1, potassium nitrate was changed to strontium acetate, and the supported concentration of strontium was 5% (complete catalyst 1 L
A catalyst (C) was obtained in the same manner except that strontium oxide was 8.3 g per unit.

【0013】実施例4 実施例1において硝酸カリウムを酢酸バリウムに変え、
バリウムの担持濃度を5%(完全触媒1L当り酸化バリ
ウム7.8 g)にした以外同様にして触媒(D)を得た。
Example 4 In Example 1, potassium nitrate was changed to barium acetate,
A catalyst (D) was obtained in the same manner except that the supported concentration of barium was changed to 5% (barium oxide: 7.8 g per 1 L of the complete catalyst).

【0014】実施例5 実施例1において硝酸パラジウム溶液の代わりにジニト
ロジアンミン白金溶液を用い白金の担持濃度を1%にし
た以外同様にして触媒(E)得た。触媒(E)における
白金量は1.8 g/個になっていた。
Example 5 A catalyst (E) was obtained in the same manner as in Example 1 except that a dinitrodiammine platinum solution was used in place of the palladium nitrate solution and the supported concentration of platinum was set to 1%. The amount of platinum in the catalyst (E) was 1.8 g / piece.

【0015】実施例6 実施例5において硝酸カリウムを硝酸セシウムに変えセ
シウムの担持濃度を5%(完全触媒1L当り酸化セシウ
ム7.4 g)にした以外同様にして触媒(F)を得た。
Example 6 A catalyst (F) was obtained in the same manner as in Example 5 except that potassium nitrate was changed to cesium nitrate and the supported concentration of cesium was changed to 5% (7.4 g of cesium oxide per 1 L of the complete catalyst).

【0016】実施例7 実施例5において硝酸カリウムをを酢酸ストロンチウム
に変え、ストロンチウムの担持濃度を5%(完全触媒1
L当り酸化ストロンチウム8.3 g)にした以外同様にし
て触媒(G)を得た。
Example 7 In Example 5, potassium nitrate was changed to strontium acetate, and the supported concentration of strontium was 5% (complete catalyst 1
A catalyst (G) was obtained in the same manner except that the amount of strontium oxide was 8.3 g per L.

【0017】実施例8 実施例5において硝酸カリウムを酢酸バリウムに変え、
バリウムの担持濃度を5%(完全触媒1L当り酸化バリ
ウム7.8 g)にした以外同様にして触媒(H)を得た。
Example 8 In Example 5, potassium nitrate was changed to barium acetate,
A catalyst (H) was obtained in the same manner except that the supported concentration of barium was 5% (barium oxide: 7.8 g per 1 L of the complete catalyst).

【0018】比較例1 実施例1において硝酸カリウムを用いない以外同様にし
て触媒(I)を得た。
Comparative Example 1 A catalyst (I) was obtained in the same manner as in Example 1 except that potassium nitrate was not used.

【0019】比較例2 実施例1において硝酸カリウムを用いず、硝酸パラジウ
ム溶液をジニトロジアンミン白金溶液に変え、白金担持
濃度を1%にした以外同様にして触媒(J)を得た。触
媒(J)における白金量は1.8 g/個になっていた。
Comparative Example 2 A catalyst (J) was obtained in the same manner as in Example 1 except that potassium nitrate was not used, the palladium nitrate solution was changed to a dinitrodiammine platinum solution, and the platinum supported concentration was set to 1%. The amount of platinum in the catalyst (J) was 1.8 g / piece.

【0020】試験例 前記実施例1〜8および比較例1,2の触媒について、
以下の条件で耐久後活性評価を行なった。
Test Example Regarding the catalysts of Examples 1 to 8 and Comparative Examples 1 and 2,
Activity evaluation after endurance was performed under the following conditions.

【0021】[0021]

【表1】 [Table 1]

【0022】評価結果は表1に示した。比較例に比べて
実施例は触媒活性が高く本発明の効果が確認できた。尚
実施例1〜4と比較例1は白金族元素としてパラジウム
を用い、実施例5〜8と比較例2は白金族元素として白
金を用いた触媒の結果を示す。
The evaluation results are shown in Table 1. The catalytic activity of the example was higher than that of the comparative example, and the effect of the present invention was confirmed. Incidentally, Examples 1 to 4 and Comparative Example 1 show the results of the catalyst using palladium as the platinum group element, and Examples 5 to 8 and Comparative Example 2 show the results of the catalyst using platinum as the platinum group element.

【0023】[0023]

【表2】[Table 2]

【0024】[0024]

【発明の効果】以上説明してきたようにこの発明の触媒
は白金、パラジウムのうち少なくとも1種を含む触媒活
性成分担持層を有する触媒組成中に、カリウム、セシウ
ム、ストロンチウム、バリウムから成る群から選ばれた
少なくとも1種の金属の酸化物を含むことにより、従来
の触媒では吸着被毒を受けて浄化性能が低下するような
ガス雰囲気においても、この吸着被毒効果を緩和し高い
性能を維持できる。このため大きく組成が変動するエン
ジン排ガス浄化に対して従来の触媒よりも高い活性を示
すため、触媒性能の向上あるいは触媒コストの低減が図
れるという効果が得られる。
As described above, the catalyst of the present invention is selected from the group consisting of potassium, cesium, strontium and barium in the catalyst composition having the catalytically active component-supporting layer containing at least one of platinum and palladium. By including at least one kind of metal oxide, it is possible to alleviate the adsorption poisoning effect and maintain high performance even in a gas atmosphere in which the purification performance is deteriorated due to adsorption poisoning in the conventional catalyst. . Therefore, it exhibits higher activity than the conventional catalyst for purification of engine exhaust gas whose composition fluctuates greatly, so that it is possible to improve catalyst performance or reduce catalyst cost.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 触媒成分担持層を有する一体構造型触媒
において、触媒成分担持層が活性アルミナと酸化セリウ
ムに触媒成分として白金とパラジウムのうち少なくとも
1種と、カリウム、セシウム、ストロンチウムおよびバ
リウムから成る群から選ばれた少なくとも1種の金属の
酸化物が担持されて成ることを特徴とする排ガス浄化用
触媒。
1. An integrated structure type catalyst having a catalyst component supporting layer, wherein the catalyst component supporting layer comprises activated alumina and cerium oxide, and at least one of platinum and palladium as a catalyst component and potassium, cesium, strontium and barium. An exhaust gas-purifying catalyst, which comprises an oxide of at least one metal selected from the group.
JP4159416A 1992-06-18 1992-06-18 Catalyst for purification of exhaust gas Pending JPH06378A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4159416A JPH06378A (en) 1992-06-18 1992-06-18 Catalyst for purification of exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4159416A JPH06378A (en) 1992-06-18 1992-06-18 Catalyst for purification of exhaust gas

Publications (1)

Publication Number Publication Date
JPH06378A true JPH06378A (en) 1994-01-11

Family

ID=15693273

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4159416A Pending JPH06378A (en) 1992-06-18 1992-06-18 Catalyst for purification of exhaust gas

Country Status (1)

Country Link
JP (1) JPH06378A (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08299793A (en) * 1995-05-01 1996-11-19 Hitachi Ltd Catalyst for purification of exhaust gas and its production
US5756057A (en) * 1993-04-28 1998-05-26 Nippon Shokubai Co., Ltd. Method for removal of nitrogen oxides from exhaust gas
EP0848983A1 (en) * 1996-12-20 1998-06-24 Ngk Insulators, Ltd. Catalyst for exhaust gas purification and system for exhaust gas purification
EP0848984A1 (en) * 1996-12-20 1998-06-24 Ngk Insulators, Ltd. Catalyst for exhaust gas purification and system for exhaust gas purification
US5814576A (en) * 1995-11-27 1998-09-29 Nissan Motor Co., Ltd. Catalyst for purifying exhaust gas and method of producing same
US6069111A (en) * 1995-06-02 2000-05-30 Nissan Motor Co., Ltd. Catalysts for the purification of exhaust gas and method of manufacturing thereof
US6358881B1 (en) 1995-05-05 2002-03-19 W. R. Grace & Co.-Conn. Reduced NOx combustion promoter for use in FCC processes
WO2013145375A1 (en) * 2012-03-30 2013-10-03 本田技研工業株式会社 Exhaust gas purification palladium monolayer catalyst for saddle-riding-type vehicle
JP2013208547A (en) * 2012-03-30 2013-10-10 Honda Motor Co Ltd Exhaust gas cleaning catalyst
US9469444B2 (en) 2005-01-31 2016-10-18 Idemitsu Unitech Co., Ltd. Easy-open container, manufacturing method thereof and manufacturing device thereof

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5756057A (en) * 1993-04-28 1998-05-26 Nippon Shokubai Co., Ltd. Method for removal of nitrogen oxides from exhaust gas
JPH08299793A (en) * 1995-05-01 1996-11-19 Hitachi Ltd Catalyst for purification of exhaust gas and its production
US6358881B1 (en) 1995-05-05 2002-03-19 W. R. Grace & Co.-Conn. Reduced NOx combustion promoter for use in FCC processes
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