JPS60238147A - Catalyst for removing nitrogen oxide - Google Patents

Catalyst for removing nitrogen oxide

Info

Publication number
JPS60238147A
JPS60238147A JP59093349A JP9334984A JPS60238147A JP S60238147 A JPS60238147 A JP S60238147A JP 59093349 A JP59093349 A JP 59093349A JP 9334984 A JP9334984 A JP 9334984A JP S60238147 A JPS60238147 A JP S60238147A
Authority
JP
Japan
Prior art keywords
catalyst
nitrogen oxide
exhaust gas
nitrogen oxides
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
JP59093349A
Other languages
Japanese (ja)
Inventor
Yoshiyasu Fujitani
藤谷 義保
Hideaki Muraki
村木 秀昭
Koji Yokota
幸治 横田
Hirobumi Shinjo
博文 新庄
Masayuki Fukui
雅幸 福井
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 Central R&D Labs Inc
Original Assignee
Toyota Central R&D Labs Inc
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 Central R&D Labs Inc filed Critical Toyota Central R&D Labs Inc
Priority to JP59093349A priority Critical patent/JPS60238147A/en
Publication of JPS60238147A publication Critical patent/JPS60238147A/en
Pending legal-status Critical Current

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

PURPOSE:To obtain a catalyst capable of purifying nitrogen oxide in exhaust gas exhausted especially from an internal combustion engine in a wide range of an air/fuel ratio with high efficiency, by supporting the group IIIa element and Pd of the Periodic Table by a porous carrier. CONSTITUTION:The group IIIa element (e.g., Ce) and Pd of the Periodic Table are supported by a porous carrier such as alumina in such a ratio that the group IIIa element is 0.01-1.0mol per 1l of the porous carrier and Pd is 0.02-10g per 1l of said carrier. The catalyst can purify nitrogen oxide with high efficiency and especially can purify nitrogen oxide in exhaust gas of a car in a wide range of an air/fuel ratio with high efficiency. Even in such a state that oxygen is excessively present in exhaust gas, nitrogen oxide can be purified with high efficiency.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、窒素酸化物、特に内燃機関等から排出される
排気ガス中の窒素酸化物を効率良く浄化することができ
る触媒に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a catalyst that can efficiently purify nitrogen oxides, particularly nitrogen oxides in exhaust gas discharged from internal combustion engines and the like.

〔従来の技術〕[Conventional technology]

近年、自動車の内燃機関等より排出される排気ガス中に
は、窒素酸化物、−酸化炭素、炭化水素の有害成分が含
まれ、大気汚染の要因となっている。そのため、この排
気浄化が種々な方面で検討されている。
In recent years, exhaust gases emitted from internal combustion engines of automobiles contain harmful components such as nitrogen oxides, carbon oxides, and hydrocarbons, which have become a cause of air pollution. Therefore, this exhaust gas purification is being studied in various fields.

この排気浄化方法のひとつとして9本発明のごとき触媒
によυ前記有害成分を除去する触媒浄とに、また該酸素
は上記−酸化炭素と反応させて二酸化炭素に、それぞれ
変換することにより、浄化を行なう。
One of the methods for purifying this exhaust gas is to use a catalyst such as the one of the present invention to remove the above-mentioned harmful components, and to convert the oxygen into carbon dioxide by reacting with the above-mentioned carbon oxide. Do the following.

従来、上記酸化用の触媒は大きな効果を持つものが開発
されているが、窒素酸化物を処理するだめの上記還元用
触媒は十分に満足できる効果的なものがまだ開発されて
いない。
Hitherto, the above-mentioned oxidation catalysts have been developed which have great effects, but the above-mentioned reduction catalysts for treating nitrogen oxides have not yet been developed which are sufficiently effective.

すなわち、排気ガス中の窒素酸化物を浄化する触媒とし
ては、アルミナ等の多孔質体から成る担体にパラジウム
、白金、ロジウム等の貴金属を担持させた触媒が触媒活
性が高いものとして用いられている。しかし、これらの
触媒は9例えば自動車の排気力゛ス中において広い空燃
比の範囲で効率良く窒素酸化物を浄化することはできな
い。特に。
In other words, as catalysts for purifying nitrogen oxides in exhaust gas, catalysts in which precious metals such as palladium, platinum, and rhodium are supported on a carrier made of a porous material such as alumina are used because they have high catalytic activity. . However, these catalysts cannot efficiently purify nitrogen oxides over a wide range of air-fuel ratios, such as in the exhaust gas of automobiles. especially.

燃料に対する空気の割合(空燃比)が高くなると。When the ratio of air to fuel (air-fuel ratio) increases.

未燃焼成分を完全燃焼させるに必要な量よりも過剰な酸
素が含まれるようになり、このような酸素の多い状態は
、窒素酸化物の前記浄化l(は悪条件である。
Oxygen is contained in excess of the amount required to completely burn the unburned components, and such an oxygen-rich state is an adverse condition for the purification of nitrogen oxides.

つまり、酸素が過剰な条件では、排気ガス中の窒素酸化
物と反応すべき水素あるいは一酸化汰素等の還元性物質
が、酸素と優先的に反応してしまい、窒素酸化物は除去
されずに残存する。
In other words, under conditions where oxygen is excessive, hydrogen or reducing substances such as oxidant monoxide, which should react with nitrogen oxides in the exhaust gas, preferentially react with oxygen, and nitrogen oxides are not removed. remains.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

上記のととく、自動車等の排気ガス中の窒素酸化物を浄
化するためには、空燃比が高い状態においても上記浄化
を効率良く行なうことができる触媒を開発することが必
要である。
As mentioned above, in order to purify nitrogen oxides in exhaust gas from automobiles, etc., it is necessary to develop a catalyst that can perform the purification efficiently even in a state where the air-fuel ratio is high.

本発明はかかる問題点を解決すべくなされたものである
The present invention has been made to solve these problems.

〔問題点を解決するための手段〕[Means for solving problems]

してなることを特徴とするものである。 It is characterized by:

本発明において、前記の第■α族元素としては。In the present invention, the above-mentioned Group Ⅰα elements include:

スカンジウム(8c)、イツトリウム(Y)、 =77
タン(Lα)、セリウム(Oe)、プラセオジム(Fr
)、ネオジム(Nd ) 、 サマIJ ウA (8m
)。
Scandium (8c), Yttrium (Y), =77
Tan (Lα), cerium (Oe), praseodymium (Fr
), Neodymium (Nd), Summer IJ UA (8m
).

ユウロピウム(Eu)、ガドリウム(Gd ) 、チル
ビウム(Tb)、ジスプロシウム(In)、ホルミウム
(no)、エルビウム(Er)、ツリウム(Tm)lイ
ッテルビ+7ム(Yb )、yvffflム(Lu)等
があり、一般に希土類元素と呼ばれるものである。
There are europium (Eu), gadolinium (Gd), tilbium (Tb), dysprosium (In), holmium (no), erbium (Er), thulium (Tm), ytterbium (Yb), yvffflm (Lu), etc. , generally called rare earth elements.

この第mα族尤素の担持量は、多孔質担体11に対して
、0.01〜1.0モルの範囲とすることが好ましい。
The supported amount of the mα group element is preferably in the range of 0.01 to 1.0 mol based on the porous carrier 11.

0.01モル未満では十分な浄化活性がなく、第MIL
族元素を担持させたことによる効果が少ない。また、担
持量が増すにつれて浄化活性は向上するが、1.0モル
より多く担持させてもそれに見合うだけの浄化活性を得
ることができず。
If it is less than 0.01 mol, there is no sufficient purifying activity, and the number of MIL
The effect of supporting group elements is small. Further, as the supported amount increases, the purifying activity improves, but even if more than 1.0 mol is supported, a commensurate purifying activity cannot be obtained.

更に共存するパラジウムの触媒作用をも阻害してしまう
Furthermore, it also inhibits the catalytic action of coexisting palladium.

また、多孔質担体に担持するパラジウムも窒素酸化物の
浄化を行なう触媒成分として働く。この担持量は、多孔
質担体11に対17て、1102〜10fの範囲内とす
ることが好ましい。該担持量が0、021未満の場合に
は、前記浄化活性が低くなり、また10gより多い場合
には、それ以上担持させてもそれに見合うだけの活性の
向上が見られない。
Furthermore, palladium supported on the porous carrier also acts as a catalyst component for purifying nitrogen oxides. The amount supported is preferably within the range of 1102 to 10 f per 17 of the porous carrier 11. If the supported amount is less than 0.021 g, the purification activity will be low, and if it is more than 10 g, no commensurate improvement in activity will be observed even if the supported amount is more than 10 g.

本発明における担体としては、アルミナ(A40、)、
マグネシア(MgO) 、アルミナ・マグネV 7 (
MgAj?t 04 ) スピネル、ジy=+=7(Z
r02)@があり、1111媒活性を向トさせるために
多孔質体とする。該多孔質体は、その原料粉末を焼結し
た焼結体が好ましい。この焼結体は強度も強く9機械的
耐久性が大きい。
The carrier in the present invention includes alumina (A40),
Magnesia (MgO), Alumina Magne V 7 (
MgAj? t 04 ) Spinel, diy=+=7(Z
r02) @, and it is made into a porous body to improve the 1111 media activity. The porous body is preferably a sintered body obtained by sintering the raw material powder. This sintered body has high strength and high mechanical durability.

上記多孔質担体に第■α族元素及びパラジウムを担持さ
せる方法は次のようにして行なうのが望ましい。担体へ
の第■α族元素の担持は、硝酸塩。
The method for supporting the group (1) alpha group element and palladium on the porous carrier is preferably carried out as follows. ■ The α-group element is supported on the carrier using nitrate.

塩化物等の第■a族元素の化合物を水、アルコール等の
溶媒に溶かし、該溶液中に上記担体を浸漬して担体中に
該溶液を含浸せしめ、乾燥後加熱して第■α族元素を担
体中に含浸担持せしめることにより行なう。また、パラ
ジウムの担持も、上記と同様にして行なう。なお、第■
α族元素の化合物とパラジウムとを含む溶液に担体を浸
漬して。
A compound of a group IV element such as a chloride is dissolved in a solvent such as water or alcohol, and the carrier is immersed in the solution to impregnate the carrier with the solution. After drying, the compound is heated to form a group IV element. This is carried out by impregnating and supporting a carrier. Further, palladium is also supported in the same manner as above. In addition, Part ■
The carrier is immersed in a solution containing an α-group element compound and palladium.

担体中に該溶液を含浸させてもよい。The solution may be impregnated into a carrier.

また1本発明にかかる触媒は0粒状体、ペレット状体、
ハニカム状体等、その形状、構造を問わないが、そのう
ちハニカム状構造体とした場合が。
In addition, the catalyst according to the present invention is a granular body, a pellet-like body,
Although its shape and structure are not limited, such as a honeycomb-like structure, there are cases where it is a honeycomb-like structure.

触媒の単位容積当りの表面積が増大しており、特に浄化
活性が亮い。
The surface area per unit volume of the catalyst is increased, and the purification activity is particularly high.

〔発明の効果〕〔Effect of the invention〕

本発明の触媒によれば、高能率で窒素酸化物を浄化する
ことができ、特に自動車排気ガス中の窒素酸化物を広い
空燃比の範囲において高能率で浄化することができる。
According to the catalyst of the present invention, nitrogen oxides can be purified with high efficiency, and in particular nitrogen oxides in automobile exhaust gas can be purified with high efficiency over a wide range of air-fuel ratios.

また、排気ガス中に酸素が過剰に存在する状態において
も、窒素酸化物を高能率で浄化するととができる。この
理由は明確ではないが、第■α族元素の作用により、多
量の窒素酸化物が触媒表面上に吸着され、酸素濃度が高
い状態においても。
Further, even in a state where an excessive amount of oxygen exists in the exhaust gas, nitrogen oxides can be purified with high efficiency. Although the reason for this is not clear, a large amount of nitrogen oxides are adsorbed on the catalyst surface due to the action of the α-group elements, even when the oxygen concentration is high.

水素あるいは一酸化伏素等の還元性物質が選択的に、こ
の窒素酸化物と反応するためと考えられる。
It is thought that this is because reducing substances such as hydrogen or arsenic monoxide selectively react with this nitrogen oxide.

なお2本発明にかかる触媒は、自動車等の内燃機関のみ
ならず、硝酸工場などの排気ガス中の窒素酸化物の浄化
用触媒として使用することができる。
Note that the catalyst according to the present invention can be used not only in internal combustion engines such as automobiles, but also as a catalyst for purifying nitrogen oxides in exhaust gas from nitric acid factories and the like.

〔実施例〕〔Example〕

以下1本発明の詳細な説明する。 The present invention will be explained in detail below.

担体としてのα−アルミナ球状多孔質体を所定濃度の第
■α族元素の硝酸塩水溶液に含浸せしめ。
An α-alumina spherical porous body serving as a carrier is impregnated with an aqueous solution of a nitrate of a group ① α element at a predetermined concentration.

乾燥後600°Cで6時間大気中で加熱して、第■α族
元素の硝酸塩を第■α族元素に分解させて。
After drying, it was heated in the air at 600°C for 6 hours to decompose the nitrates of group ①α elements into group ①α elements.

担体11当り第pla族元素を0.1 m4kg担持さ
せた。続いて、パラジウムの硝酸塩水溶液に上記担体を
含浸せしめ、乾燥後600°Cで3時間大気中で加熱し
て担体11当りパラジウムを1f担持させて2本発明に
かかる触媒(第1表の触媒A1〜15)を得た。該触媒
における第■α族元素の種類を第1表に示す。また、比
較のため、第■α族元素を担持することなく、パラジウ
ムのみを上記と同様にして担持させた比較用触媒(触媒
A31)もlI4製した。
0.1 m4kg of the Pla group element was supported on each carrier 11. Subsequently, the above-mentioned carrier was impregnated with an aqueous solution of palladium nitrate, and after drying, it was heated in the air at 600°C for 3 hours to support 1f of palladium per 11 carriers. ~15) was obtained. Table 1 shows the types of group ①α elements in the catalyst. In addition, for comparison, a comparative catalyst (catalyst A31) was also prepared in which only palladium was supported in the same manner as above without supporting the group ①α element (catalyst A31).

得られた触媒についての浄化活性評価を行なうに際し、
まず予め触媒の耐久試験を行なった。即ち、上記触媒を
理論空燃比(約14.6 )で運転する内燃機関(ガソ
リンを燃料とするエンジン)からの排気ガス中に温度7
50℃、空間速度25000/時で、100時間放置し
て耐久試験を行なった。
When evaluating the purification activity of the obtained catalyst,
First, a durability test of the catalyst was conducted in advance. That is, the temperature of the exhaust gas from an internal combustion engine (an engine using gasoline as fuel) in which the catalyst is operated at a stoichiometric air-fuel ratio (approximately 14.6)
A durability test was conducted at 50° C. and a space velocity of 25,000/hour for 100 hours.

次に、上記浄化活性評価のため、上記触媒について窒素
酸化物(NOx )及び酸素(02)の除去率を測定し
た。
Next, in order to evaluate the purification activity, the nitrogen oxide (NOx) and oxygen (02) removal rates of the catalyst were measured.

即ち、上記触媒を反応管としての石英管に充填し、室温
から4°C/minの昇温速度で500℃まで加熱しな
がら、この石英管に空間速度50000/時、理論空燃
比で運転した自動車の内燃機関からの排気ガスを導入し
た。上記運転時における排草ガス中の各成分の濃度は、
容量比で、窒素酸化物0.1%、−酸化炭素0.8%、
炭化水素α12%。
That is, the above catalyst was filled in a quartz tube as a reaction tube, and the quartz tube was operated at a space velocity of 50,000/hour and a stoichiometric air-fuel ratio while heating from room temperature to 500° C. at a temperature increase rate of 4° C./min. Exhaust gas from automobile internal combustion engines was introduced. The concentration of each component in the exhaust gas during the above operation is as follows:
By volume ratio, nitrogen oxide 0.1%, -carbon oxide 0.8%,
Hydrocarbon α12%.

二酸化灰素12%、水素0.2%、酸素α68%。12% ash dioxide, 0.2% hydrogen, 68% oxygen α.

水16%、残部窒素であった。その後、各触媒に対して
、NOx及び02の除去率を測定した。
It was 16% water and the balance was nitrogen. Thereafter, the NOx and 02 removal rates were measured for each catalyst.

第1図は、触媒層2の触媒を例として、触媒層温度を横
軸に、NOx、0.の除去率を縦軸にとって、浄化活性
を図示したものである。更に、その結果を各触媒層にお
けるNOxとO−との除去率の選択性で整理して、第2
図に01除去率を横軸に。
FIG. 1 takes the catalyst of the catalyst layer 2 as an example, and plots the temperature of the catalyst layer on the horizontal axis, NOx, 0. The purification activity is illustrated with the vertical axis representing the removal rate. Furthermore, the results were organized in terms of the selectivity of the NOx and O- removal rates in each catalyst layer, and the second
In the figure, 01 removal rate is plotted on the horizontal axis.

NOx除去率を縦軸にとって図示した。第2図において
、対角線と上部の曲線とで囲まれる部分(NOxの除去
率の優れた部分)の面積8(NOx)。
The NOx removal rate is plotted on the vertical axis. In FIG. 2, area 8 (NOx) of the part surrounded by the diagonal line and the upper curve (the part with excellent NOx removal rate).

及び対角線と下部の曲線とで囲まれる部分(02の除去
率の優れた部分)の面積5(01)を測定して。
Then, measure the area 5 (01) of the part surrounded by the diagonal line and the lower curve (the part with excellent removal rate of 02).

その比8 (NOx )/8 (Os )をめた。S 
(N0x)/5(O2)比の値が大きい程、NOxの除
去率が高いことを示す。
The ratio was set at 8 (NOx)/8 (Os). S
The larger the value of the (N0x)/5(O2) ratio, the higher the NOx removal rate.

また、比較触媒(触媒層81)に対する測定結果より、
触媒層温度とNO,,0,の除去率との関係図を第3図
に、NOxと0寞との除去率の選択性を表わす図を第4
図に示した。また、第4図より上記の8(NOx)/8
 (0,)比をめた。
Also, from the measurement results for the comparative catalyst (catalyst layer 81),
Figure 3 shows the relationship between the catalyst layer temperature and the removal rate of NO,,0, and Figure 4 shows the selectivity of the removal rate of NOx and NOx.
Shown in the figure. Also, from Figure 4, the above 8(NOx)/8
We calculated the (0,) ratio.

各触媒についての8(NOx)/8 (OM )比を測
定して、その結果を第2表に示す。
The 8(NOx)/8(OM) ratio for each catalyst was measured and the results are shown in Table 2.

第2表より明らかなごとく1本発明にかかる触媒は8 
(N0x)/8 (o、)比が0.51〜1.68とい
う高い値を示すのに比し、比較触媒(A81)は0,1
3という低い値を示し2本発明触媒は著し
As is clear from Table 2, the catalyst according to the present invention is 8
(N0x)/8 (o,) ratio shows a high value of 0.51 to 1.68, while the comparative catalyst (A81) has a ratio of 0.1 to 1.68.
The catalyst of the present invention showed a significantly low value of 3.

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

第1図及び第5図は実施例における触KA2及び81の
NOxと0鵞の除去率曲線、第2図及び第4図は触媒F
X2及び81のNOxと0!との除去率関係曲線を示す
図である。 出願人 株式会社 豊田中央研究所 代理人 弁理士高橋祥 泰 (外2名) 第7図 第3図 角良殊ル 刃り角LrCノ 第21iJ 第4図 (ト 障、#’!/%)
Figures 1 and 5 are the NOx and 0 removal rate curves for catalysts KA2 and KA81 in Examples, and Figures 2 and 4 are for catalyst F.
X2 and 81 NOx and 0! It is a figure which shows the removal rate relationship curve with. Applicant Toyota Central Research Institute Co., Ltd. Patent Attorney Yoshiyasu Takahashi (2 others)

Claims (4)

【特許請求の範囲】[Claims] (1)多孔質担体に周期律表の第1[A族元素及びパラ
ジウムを担持してなることを特徴とする窒素酸化物除去
用触媒。
(1) A catalyst for removing nitrogen oxides, comprising a porous carrier supporting an element of group 1 [A of the periodic table] and palladium.
(2)上記多孔質担体は、アルミナ、マグネシア。 アルミナ・マグネシアスピネA/、ジpコニアの1種ま
たは2種以上である特許請求の範囲第(1)項記載の窒
素酸化物除去用触媒。
(2) The porous carrier is alumina or magnesia. The catalyst for removing nitrogen oxides according to claim 1, which is one or more of alumina, magnesia spine A/, and zipconia.
(3)上記周期律表の第■α族元素は、多孔質担体11
に001ないし1.0モル担持してなる特許請求の範囲
第(1)項記載の窒素酸化物除去用触媒。
(3) Group ■α elements of the periodic table are contained in the porous carrier 11
The catalyst for removing nitrogen oxides according to claim (1), wherein 0.001 to 1.0 mol of nitrogen oxides are supported on the catalyst.
(4)上記パラジウムは、多孔質担体11にα02ない
し10g担持してなる特許請求の範囲第(1)項記載の
窒素酸化物除去用触媒。
(4) The catalyst for removing nitrogen oxides according to claim (1), wherein the palladium is supported on a porous carrier 11 in an amount of α02 to 10 g.
JP59093349A 1984-05-10 1984-05-10 Catalyst for removing nitrogen oxide Pending JPS60238147A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59093349A JPS60238147A (en) 1984-05-10 1984-05-10 Catalyst for removing nitrogen oxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59093349A JPS60238147A (en) 1984-05-10 1984-05-10 Catalyst for removing nitrogen oxide

Publications (1)

Publication Number Publication Date
JPS60238147A true JPS60238147A (en) 1985-11-27

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Family Applications (1)

Application Number Title Priority Date Filing Date
JP59093349A Pending JPS60238147A (en) 1984-05-10 1984-05-10 Catalyst for removing nitrogen oxide

Country Status (1)

Country Link
JP (1) JPS60238147A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05220396A (en) * 1992-02-13 1993-08-31 Agency Of Ind Science & Technol Waste gas purifying catalyst

Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4956892A (en) * 1972-07-14 1974-06-03
JPS4990695A (en) * 1972-12-19 1974-08-29
JPS55155739A (en) * 1979-05-23 1980-12-04 Toyota Central Res & Dev Lab Inc Exhaust gas purifying catalyzer
JPS5621646A (en) * 1979-07-28 1981-02-28 Toyota Motor Corp Oxidation catalyst for cleaning automobile exhaust gas
JPS5687430A (en) * 1979-12-19 1981-07-16 Toyota Central Res & Dev Lab Inc Catalyst for purifying exhaust gas
JPS56124442A (en) * 1980-03-06 1981-09-30 Toyota Central Res & Dev Lab Inc Catalyst for cleaning of exhaust gas
JPS5732733A (en) * 1980-08-05 1982-02-22 Toyota Central Res & Dev Lab Inc Catalyst for purification of waste gas and method for purification of waste gas
JPS5735939A (en) * 1980-08-13 1982-02-26 Toyota Central Res & Dev Lab Inc Cleaning catalyst for exhaust gas
JPS5756041A (en) * 1980-09-19 1982-04-03 Mitsui Mining & Smelting Co Ltd Palladium catalyst
JPS5787839A (en) * 1980-11-20 1982-06-01 Toyota Motor Corp Catalyst of monolithic construction type for purification of waste gas
JPS57119838A (en) * 1981-01-20 1982-07-26 Mitsui Mining & Smelting Co Ltd Production of palladium catalyst
JPS5836634A (en) * 1981-08-29 1983-03-03 Toyota Central Res & Dev Lab Inc Exhaust gas purifying catalyst

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4956892A (en) * 1972-07-14 1974-06-03
JPS4990695A (en) * 1972-12-19 1974-08-29
JPS55155739A (en) * 1979-05-23 1980-12-04 Toyota Central Res & Dev Lab Inc Exhaust gas purifying catalyzer
JPS5621646A (en) * 1979-07-28 1981-02-28 Toyota Motor Corp Oxidation catalyst for cleaning automobile exhaust gas
JPS5687430A (en) * 1979-12-19 1981-07-16 Toyota Central Res & Dev Lab Inc Catalyst for purifying exhaust gas
JPS56124442A (en) * 1980-03-06 1981-09-30 Toyota Central Res & Dev Lab Inc Catalyst for cleaning of exhaust gas
JPS5732733A (en) * 1980-08-05 1982-02-22 Toyota Central Res & Dev Lab Inc Catalyst for purification of waste gas and method for purification of waste gas
JPS5735939A (en) * 1980-08-13 1982-02-26 Toyota Central Res & Dev Lab Inc Cleaning catalyst for exhaust gas
JPS5756041A (en) * 1980-09-19 1982-04-03 Mitsui Mining & Smelting Co Ltd Palladium catalyst
JPS5787839A (en) * 1980-11-20 1982-06-01 Toyota Motor Corp Catalyst of monolithic construction type for purification of waste gas
JPS57119838A (en) * 1981-01-20 1982-07-26 Mitsui Mining & Smelting Co Ltd Production of palladium catalyst
JPS5836634A (en) * 1981-08-29 1983-03-03 Toyota Central Res & Dev Lab Inc Exhaust gas purifying catalyst

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05220396A (en) * 1992-02-13 1993-08-31 Agency Of Ind Science & Technol Waste gas purifying catalyst

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