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JPS5930459B2 - Catalyst for exhaust gas treatment - Google Patents
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JPS5930459B2 - Catalyst for exhaust gas treatment - Google Patents

Catalyst for exhaust gas treatment

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Publication number
JPS5930459B2
JPS5930459B2 JP51150586A JP15058676A JPS5930459B2 JP S5930459 B2 JPS5930459 B2 JP S5930459B2 JP 51150586 A JP51150586 A JP 51150586A JP 15058676 A JP15058676 A JP 15058676A JP S5930459 B2 JPS5930459 B2 JP S5930459B2
Authority
JP
Japan
Prior art keywords
catalyst
weight
ruthenium
layer
exhaust gas
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.)
Expired
Application number
JP51150586A
Other languages
Japanese (ja)
Other versions
JPS5375188A (en
Inventor
健治 大久保
光昭 河村
和則 井原
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.)
Mazda Motor Corp
Original Assignee
Toyo Kogyo 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 Toyo Kogyo Co Ltd filed Critical Toyo Kogyo Co Ltd
Priority to JP51150586A priority Critical patent/JPS5930459B2/en
Publication of JPS5375188A publication Critical patent/JPS5375188A/en
Publication of JPS5930459B2 publication Critical patent/JPS5930459B2/en
Expired legal-status Critical Current

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

Description

【発明の詳細な説明】 この発明は内燃機関の排ガスを浄化処理するための触媒
に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a catalyst for purifying exhaust gas from an internal combustion engine.

内燃機関の排ガス中に含有する窒素酸化物(NOx)炭
化水素(HC)、一酸化炭素(CO)の有害成分を浄化
処理するために触媒コンバータが使用されており、これ
らの触媒として種々のものが提案されている。
Catalytic converters are used to purify harmful components such as nitrogen oxides (NOx), hydrocarbons (HC), and carbon monoxide (CO) contained in the exhaust gas of internal combustion engines. is proposed.

窒素酸化物は還元反応によって処理され、炭化水素、一
酸化炭素は酸化反応によって処理されるため、両反応を
満足させるための適当な触媒は未だなく、従って還元性
触媒と酸化性触媒を併用するのが一般的である。
Nitrogen oxides are treated by a reduction reaction, and hydrocarbons and carbon monoxide are treated by an oxidation reaction.Therefore, there is no suitable catalyst that can satisfy both reactions, so a combination of a reducing catalyst and an oxidizing catalyst is used. is common.

還元性触媒としてルテニウムは、還元雰囲気中における
NOxの浄化に対する活性が犬であり、かつ還元作用に
よるアンモニアの生成が少なくて窒素への還元率が高い
ので優れた触媒であるが、HClC0に対する酸化性能
は十分でない。
As a reducing catalyst, ruthenium is an excellent catalyst because it has the highest activity for purifying NOx in a reducing atmosphere, produces less ammonia due to reduction action, and has a high reduction rate to nitrogen, but it has poor oxidation performance against HClC0. is not enough.

従って冷間始動時の暖機対策として濃混合気を使用した
場合に排ガス中に多量に含有されているHC,COの処
理対策として、上記ルテニウムに、白金、パラジウム等
の酸化性能触媒を併用している。
Therefore, when a rich mixture is used as a warm-up measure during a cold start, an oxidizing performance catalyst such as platinum or palladium is used in combination with the above ruthenium to treat HC and CO that are contained in large amounts in the exhaust gas. ing.

また、ルテニウムは、酸化雰囲気中で使用すると酸化物
に変化して蒸散する性質を有しているので、その対策と
して、アルカリ土類金属その他の卑金属の酸化物を安定
剤として使用することが知られている。
Furthermore, when ruthenium is used in an oxidizing atmosphere, it changes into an oxide and evaporates, so as a countermeasure, it is known that oxides of alkaline earth metals and other base metals are used as stabilizers. It is being

上記の知見によって、アルミナなどの担体に、白金やパ
ラジウム等の貴金属を0.1〜3%担持させた貴金属触
媒と、酸化第二鉄35〜60モル%、二酸化マンガン、
酸化第二銅、酸化クロム、酸化モリブデンなどから選ば
れた金属酸化物65〜40モル%及びルテニウムを含み
部分的にスピネル構造を有する金属酸化物焼結体触媒と
を混合したものが提案されている(特開昭50−131
668号公報参照)。
Based on the above findings, a noble metal catalyst in which 0.1 to 3% of a noble metal such as platinum or palladium is supported on a support such as alumina, 35 to 60 mol% of ferric oxide, manganese dioxide,
A mixture of 65 to 40 mol% of a metal oxide selected from cupric oxide, chromium oxide, molybdenum oxide, etc. and a metal oxide sintered catalyst containing ruthenium and partially having a spinel structure has been proposed. (Unexamined Japanese Patent Publication No. 50-131
(See Publication No. 668).

しかし上記提案の触媒は、ルテニウムの安定性が未だ十
分でなく、また安定剤の添加によってルテニウムの活性
が低下し、更に白金、パラジウム等の貴金属触媒の混合
によってルテニウムの特長であるNOxの窒素還元率を
低下してアンモニアが生成するなどの問題がある。
However, in the catalyst proposed above, the stability of ruthenium is still insufficient, and the activity of ruthenium decreases due to the addition of a stabilizer, and furthermore, the addition of a noble metal catalyst such as platinum or palladium results in the nitrogen reduction of NOx, which is a characteristic of ruthenium. There are problems such as lowering the rate and producing ammonia.

本発明者らは、上記の問題を解決するために鋭意研究し
た結果、この発明を完成するに至ったのである。
The present inventors have completed this invention as a result of intensive research to solve the above problems.

すなわちこの発明は、粒状の多孔性セラミック担体上に
、全触媒に対して、マンガン、銅、コバルト、ニッケル
、クロム、バリウム、カルシウム及びマグネシウムのう
ちの少なくとも1種の金属の酸化物を含む酸化鉄0.5
〜30重量%を内部層トシ、ルテニウム0.001〜0
.5重量%を中間層とし、白金又はパラジウム0.00
1〜0.5重量%を外部層としてそれぞれが順次に含浸
被覆されたことを特徴とする排ガス処理用触媒である。
That is, the present invention provides iron oxide containing an oxide of at least one metal selected from manganese, copper, cobalt, nickel, chromium, barium, calcium and magnesium for the total catalyst on a granular porous ceramic support. 0.5
~30% by weight in the inner layer, ruthenium 0.001~0
.. 5% by weight as an intermediate layer, platinum or palladium 0.00%
The catalyst for exhaust gas treatment is characterized in that each layer is sequentially impregnated and coated with 1 to 0.5% by weight of the outer layer.

この発明に使用される粒状の多孔性セラミック担体は、
アルミナ、アルミナ・シリカ、ムライトコープイライト
、炭化ケイ素等からなる多孔性のもので、その粒度は2
〜3mmのものが好ましい。
The granular porous ceramic carrier used in this invention is
It is a porous material made of alumina, alumina-silica, mullite copillite, silicon carbide, etc., and its particle size is 2.
~3 mm is preferred.

この触媒の内部層を形成する酸化鉄は、マンガン、銅、
コバルト、ニッケル、クロム、バリウム、カルシウム及
びマグネシウムから選ばれた少なくとも1種の金属の酸
化物と、酸化鉄との混合物であって部分的にスピネル構
造を有している焼結体である。
The iron oxides that form the inner layer of this catalyst include manganese, copper,
It is a sintered body that is a mixture of an oxide of at least one metal selected from cobalt, nickel, chromium, barium, calcium, and magnesium and iron oxide, and partially has a spinel structure.

上記マンガン等の金属酸化物と酸化鉄の割合は、前者が
20〜70モル%、後者が80〜30モル%であること
力士好ましい。
For sumo wrestlers, the ratio of the metal oxide such as manganese and iron oxide is preferably 20 to 70 mol% for the former and 80 to 30 mol% for the latter.

上記内部層を担体に担持させるに、十分に乾燥した担体
を上記金属塩の水溶液に浸漬し、次いで100〜200
℃で乾燥したのち、不活性ガスあるいは空気中で600
〜1300℃に焼成を行なうものである。
To support the inner layer on the carrier, the sufficiently dried carrier is immersed in an aqueous solution of the metal salt, and then
After drying at ℃, 600℃ in inert gas or air.
Firing is performed at ~1300°C.

金属塩の種類、水溶液の濃度、乾燥及び焼成の諸条件は
、□焼成後の酸化物の結晶が部分的にスピネル構造を有
するように適宜に選択される。
The type of metal salt, the concentration of the aqueous solution, and the drying and firing conditions are appropriately selected so that the oxide crystals after firing partially have a spinel structure.

上記担体に含浸被覆させた内部層の上にルテニウムの中
間層を被覆するには、ルテニウム塩化物のようなハロゲ
ン化物、:あるいは水溶性塩の水溶液に上記の内部層を
被覆した担体を浸漬し、100〜200℃で乾燥したの
ち、不活性ガスあるいは還元性ガスの気流中で500〜
800℃に加熱処理を行なう。
To coat the inner layer of ruthenium on the inner layer impregnated on the carrier, the carrier coated with the inner layer is immersed in an aqueous solution of a halide such as ruthenium chloride, or a water-soluble salt. After drying at 100-200℃, drying at 500-200℃ in a stream of inert gas or reducing gas.
Heat treatment is performed at 800°C.

□次いで、該中間層の上に白金又はパラジウ
ムの外部層を含浸被覆するには、上記中間層の含浸被覆
と同様にして行なう。
□Then, the outer layer of platinum or palladium is impregnated onto the intermediate layer in the same manner as the impregnation coating of the intermediate layer described above.

上記のようにして担体に順次含浸被覆される各層の量は
、全触媒量に対して、内部層が0.5〜30重量%、中
間層及び外部層がそれぞれ0.001〜0.5重量%、
好ましくは0.02〜0.2重量%である。
The amount of each layer sequentially impregnated and coated on the carrier as described above is 0.5 to 30% by weight for the inner layer and 0.001 to 0.5% by weight for each of the intermediate layer and the outer layer, based on the total amount of catalyst. %,
Preferably it is 0.02 to 0.2% by weight.

内部層が0.5重量%未満の場合は、中間層のルテニウ
ムが十分に安定化されず、また30重量%を越える場合
は、触媒粒子の強度が著しく低下して破損し易くなり、
いずれの場合も耐久試験後の浄化率が低下する。
If the content of the inner layer is less than 0.5% by weight, the ruthenium in the intermediate layer will not be sufficiently stabilized, and if it exceeds 30% by weight, the strength of the catalyst particles will be significantly reduced and they will be easily damaged.
In either case, the purification rate after the durability test decreases.

中間層が0.001重量%未満の場合は、NOxに対す
る浄化性能が不足し、また0、5重量%を越えてもさほ
ど浄化性能が増加するものでなく却ってコスト高となる
If the content of the intermediate layer is less than 0.001% by weight, the purification performance against NOx will be insufficient, and if it exceeds 0.5% by weight, the purification performance will not increase much and the cost will increase.

外部層が0.001重量%未満の場合は、炭化水素、一
酸化炭素に対する浄化性能が不足し、また0、5重量%
を越えても、ルテニウムと同様に、さほど浄化性能が増
加するものでなく却ってコスト高となる。
If the outer layer contains less than 0.001% by weight, the purification performance against hydrocarbons and carbon monoxide will be insufficient;
Even if it exceeds ruthenium, as with ruthenium, the purification performance will not increase much and the cost will increase.

この発明の触媒は、還元雰囲気中におけるNOxの浄化
性能が向上し、かつNOxから窒素への選択的還元率が
向上していると共に、酸化雰囲気中におけるHC,CO
の浄化性能が向上している。
The catalyst of the present invention has improved NOx purification performance in a reducing atmosphere and improved selective reduction rate from NOx to nitrogen, as well as improved HC and CO removal in an oxidizing atmosphere.
Purification performance has been improved.

そしてこの触媒の特筆すべきことは、耐久試験後におけ
るNOxの浄化性能の低下が小さくて、長期にわたって
使用できることである。
What is noteworthy about this catalyst is that the NOx purification performance decreases little after the durability test, and it can be used for a long period of time.

以下にこの発明の実施例について説明する。Examples of the present invention will be described below.

なお、実症例中の部、%は特に断わりのない限り重量基
準で示したものである。
In addition, parts and percentages in actual cases are expressed on a weight basis unless otherwise specified.

実施例 1 硝酸第?鉄(Fe (NO3) 2−6H20)と硝酸
マンガン(Mn (N03) 2 ・6 H20)を脱
イオン水に溶解しF e (NOa ) 2が20%、
Mn (NOa ) 2が10%になるように水溶液を
調製し、この水溶液に、十分に乾燥したアルミナ製粒状
担体(粒径3朋、充填比重0.70)を浸漬して担体に
水溶液を十分に浸透させた後、担体を引上げて150℃
、4時間乾燥し、次いで窒素気流中で900℃、2時間
焼成処理を行なった。
Example 1 Nitric acid No. 1? Iron (Fe (NO3) 2-6H20) and manganese nitrate (Mn (N03) 2 ・6 H20) were dissolved in deionized water to give 20% Fe (NOa) 2,
An aqueous solution was prepared so that the Mn (NOa) 2 content was 10%, and a sufficiently dried alumina granular carrier (particle size 3, filling specific gravity 0.70) was immersed in this aqueous solution, and the aqueous solution was sufficiently applied to the carrier. After infiltrating the carrier, the carrier was pulled up and heated to 150°C.
, dried for 4 hours, and then fired at 900° C. for 2 hours in a nitrogen stream.

上記焼成処理後、冷却した担体を、塩化ルテニウム(R
uC13)の濃度0.5%の水溶液に浸漬した後、20
0℃、2時間乾燥し、次いで水素気流中で600℃、2
時間還元処理を行なって中間層を形成した。
After the above calcination treatment, the cooled carrier was heated to ruthenium chloride (R
After immersion in an aqueous solution of uC13) with a concentration of 0.5%,
Dry at 0°C for 2 hours, then dry at 600°C for 2 hours in a hydrogen stream.
A time reduction treatment was performed to form an intermediate layer.

次に、上記中間層を含浸被覆した担体を、塩化白金酸(
H2PtCl4・6H20)の濃度0.52%の溶液に
浸漬し、上記中間層と同様な条件で還元処理して外部層
を形成した。
Next, the carrier impregnated with the above intermediate layer was coated with chloroplatinic acid (
The outer layer was immersed in a solution of H2PtCl4.6H20) with a concentration of 0.52% and subjected to reduction treatment under the same conditions as the intermediate layer.

得られた触媒の内部層は、Fe0.9%、Mn094%
、中間層はRuO,05%、外部層はPiO905%で
あって、Fe、Mnはともに酸化物として存在し、その
一部がスピネル構造を有していることがX線回折試験に
よって確認された。
The inner layer of the obtained catalyst contains 0.9% Fe and 94% Mn.
An X-ray diffraction test confirmed that the intermediate layer was made of 05% RuO and the outer layer was made of 905% PiO, and that both Fe and Mn existed as oxides, and a part of them had a spinel structure. .

実施例 2 上記実施例1において、外部層の塩化白金酸の代わりに
塩化パラジウム(PdC12)を使用した以外は、実施
例1と同様にして、Fe0.9%、M n 0.4%、
Ru0.05%、Pd0.05%の触媒を得た。
Example 2 In the same manner as in Example 1, except that palladium chloride (PdC12) was used instead of chloroplatinic acid in the outer layer in Example 1, Fe0.9%, Mn 0.4%,
A catalyst containing 0.05% Ru and 0.05% Pd was obtained.

比較例 1 実施例1と同様にしてFelMnの内部層を形成した担
体に、塩化ルテニウムと塩化白金酸との混合水溶液を含
浸させてFe、Mnの内部層とRu1Pt混合の外部層
との二層の触媒を得た。
Comparative Example 1 A carrier on which an internal layer of FeIMn was formed in the same manner as in Example 1 was impregnated with a mixed aqueous solution of ruthenium chloride and chloroplatinic acid to form a two-layer structure consisting of an internal layer of Fe and Mn and an external layer of a mixture of Ru1Pt. A catalyst was obtained.

比較例 2 実施例1において、Ruとptとの被覆処理順序を逆に
して、Fe、Mnの内部層と、Ptの中間層と、Ruの
外部層の触媒を得た。
Comparative Example 2 In Example 1, the order of coating Ru and PT was reversed to obtain a catalyst including an inner layer of Fe and Mn, an intermediate layer of Pt, and an outer layer of Ru.

比較例 3 実施例1において、Ruの内部層と、FelMnの中間
層と、Ptの外部層の触媒を得た。
Comparative Example 3 In Example 1, a catalyst with an inner layer of Ru, an intermediate layer of FeIMn, and an outer layer of Pt was obtained.

比較例 4 実施例1において、Ptの内部層と、FelMnの中間
層と、Ruの外部層の触媒を得た。
Comparative Example 4 In Example 1, a catalyst with an inner layer of Pt, an intermediate layer of FeIMn, and an outer layer of Ru was obtained.

上記の実施例、比較例で得た各触媒について下記の方法
によってNOx、HClC0に対する浄化性能の評価試
験を行なった。
Evaluation tests for the purification performance of NOx and HClC0 were conducted on each of the catalysts obtained in the above Examples and Comparative Examples using the method described below.

試験に使用した合成排ガスの成分は下表の通りである。The components of the synthetic exhaust gas used in the test are shown in the table below.

ベット容積24ccの触媒に、触媒容量に対する1時間
当りの上記合成排ガスの容量を40,000とした空間
速度で通過させ、通過後のNOx。
NOx after passing through a catalyst with a bed volume of 24 cc at a space velocity where the volume of the synthetic exhaust gas per hour relative to the catalyst capacity was set to 40,000.

HC,COの濃度を測定して浄化率を算出した。The purification rate was calculated by measuring the concentrations of HC and CO.

なお、上記触媒の耐久性の評価のために、900℃の電
気炉中にいれた触媒に、空気と、5%の水素を含む窒素
ガスとを15分間サイクルで交互に12時間導入して加
熱し、この耐久試験後の触媒について上記と同様に性能
評価試験を行なった。
In order to evaluate the durability of the above catalyst, air and nitrogen gas containing 5% hydrogen were alternately introduced into the catalyst in a 900°C electric furnace in a 15 minute cycle for 12 hours. After this durability test, the catalyst was subjected to a performance evaluation test in the same manner as above.

上記評価試験の結果を第1表、第2表及び第3表に示す
The results of the above evaluation tests are shown in Tables 1, 2 and 3.

ただし、内、中、外層の行のMはFeMnを意味してい
る。
However, M in the inner, middle, and outer layer rows means FeMn.

なお第1表、第2表のNOxの浄化率の括弧書きは、窒
素(N2)への選択的還元率を示す。
Note that in Tables 1 and 2, the NOx purification rate in parentheses indicates the selective reduction rate to nitrogen (N2).

上記第1.2表でみられるように、実施例に比べて、各
比較例に共通していることは、耐久試験後のNOx浄化
率が新品のNOx浄化率に比べて小さいことである。
As can be seen in Table 1.2 above, compared to the Examples, what each Comparative Example has in common is that the NOx purification rate after the durability test is smaller than the NOx purification rate of the new product.

ルテニウムを外部層とする比較例2及び比較例4は、空
燃比14.0におけるHClC0の浄化率が低い。
Comparative Examples 2 and 4 in which ruthenium was used as the outer layer had a low HClC0 purification rate at an air-fuel ratio of 14.0.

またルテニウムを内部層とする比較例3は、NOxの浄
化率が特に低い0 なお、第3表に示すように、空燃比16.Oの場合のH
C,COの浄化率は実施例、比較例ともに大きな差がみ
られない。
Furthermore, in Comparative Example 3, in which ruthenium is used as the inner layer, the NOx purification rate is particularly low.As shown in Table 3, the air-fuel ratio is 16. H in case of O
There is no significant difference in the C and CO purification rates between the Examples and Comparative Examples.

実施例 3 実施例1の触媒の内部層のFeO,9%、Mn0.4%
のうち、MnをMnと同量のCu、Co。
Example 3 FeO, 9%, Mn 0.4% in the inner layer of the catalyst of Example 1
Among them, Mn and Cu and Co in the same amount as Mn.

Ni、Cr、BaXCaまたはMgに代えて内部層とし
、実施例1と同じ中間層Rn0.05%、外部層Pt0
.05%との触媒を作成し、これら触媒の性能評価試験
を実施例1第1表におけると同様に行ない、耐久試験後
の浄化率(資)を下記第4表に示す。
Ni, Cr, BaXCa or Mg was replaced with the inner layer, the same intermediate layer Rn0.05% and the outer layer Pt0 as in Example 1.
.. 05% and the performance evaluation test of these catalysts was conducted in the same manner as in Table 1 of Example 1. The purification rate (equity) after the durability test is shown in Table 4 below.

上記第4表に示すように耐久試験後の浄化率は、Mnが
最も良いが、他の金属においても大きな差はなく、NO
x浄化率は70%以上である。
As shown in Table 4 above, Mn has the best purification rate after the durability test, but there is no big difference among other metals, and NO
x Purification rate is 70% or more.

実施例 4 実施例1の触媒の内部層Fe0.9%、Mn0.4%の
重量を変えて実施例1第1表におけると同様にして触媒
の性能評価試験を行ない、耐久試験後の浄化率(%)を
図面の対数グラフに示した。
Example 4 A performance evaluation test of the catalyst was conducted in the same manner as in Table 1 of Example 1 by changing the weight of the inner layer of Fe0.9% and Mn0.4% of the catalyst of Example 1, and the purification rate after the durability test was (%) is shown in the logarithmic graph of the drawing.

図面で見られるように、内部層が1〜15重量%ではN
Ox浄化率が90%以上であり、0.5重量%又は30
重量%を外れた場合は急速に70%より小さくなる。
As seen in the drawings, the inner layer is 1-15% by weight of N.
Ox purification rate is 90% or more, and 0.5% by weight or 30%
If the weight % is exceeded, it rapidly becomes smaller than 70%.

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

図面は実施例4における内部層の金属酸化物量と耐久試
験後の浄化率との関係を示す対数グラフである。
The drawing is a logarithmic graph showing the relationship between the amount of metal oxide in the inner layer and the purification rate after the durability test in Example 4.

Claims (1)

【特許請求の範囲】 1 粒状の多孔性セラミック担体上に、全触媒に対して
、マンガン、銅、コバルト、ニッケル、クロム、バリウ
ム、カルシウム及びマグネシウムのうちの少なくとも1
種の金属の酸化物を含む酸化鉄0.5〜30重量%を内
部層とし、ルテニウム0.001〜0.5重量%を中間
層とし。 白金又はパラジウム0.001〜0,5重量%を外部層
としてそれぞれが順次に含浸被覆されたことを特徴とす
る排ガス処理用触媒。
[Scope of Claims] 1. At least one of manganese, copper, cobalt, nickel, chromium, barium, calcium and magnesium, based on the total catalyst, on a granular porous ceramic support.
The inner layer contains 0.5 to 30% by weight of iron oxide containing oxides of various metals, and the intermediate layer contains 0.001 to 0.5% by weight of ruthenium. 1. A catalyst for exhaust gas treatment, characterized in that each outer layer is sequentially impregnated and coated with 0.001 to 0.5% by weight of platinum or palladium.
JP51150586A 1976-12-14 1976-12-14 Catalyst for exhaust gas treatment Expired JPS5930459B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP51150586A JPS5930459B2 (en) 1976-12-14 1976-12-14 Catalyst for exhaust gas treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP51150586A JPS5930459B2 (en) 1976-12-14 1976-12-14 Catalyst for exhaust gas treatment

Publications (2)

Publication Number Publication Date
JPS5375188A JPS5375188A (en) 1978-07-04
JPS5930459B2 true JPS5930459B2 (en) 1984-07-27

Family

ID=15500115

Family Applications (1)

Application Number Title Priority Date Filing Date
JP51150586A Expired JPS5930459B2 (en) 1976-12-14 1976-12-14 Catalyst for exhaust gas treatment

Country Status (1)

Country Link
JP (1) JPS5930459B2 (en)

Also Published As

Publication number Publication date
JPS5375188A (en) 1978-07-04

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