JP3251009B2 - Exhaust gas purification catalyst - Google Patents

Exhaust gas purification catalyst

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Publication number
JP3251009B2
JP3251009B2 JP28286790A JP28286790A JP3251009B2 JP 3251009 B2 JP3251009 B2 JP 3251009B2 JP 28286790 A JP28286790 A JP 28286790A JP 28286790 A JP28286790 A JP 28286790A JP 3251009 B2 JP3251009 B2 JP 3251009B2
Authority
JP
Japan
Prior art keywords
exhaust gas
palladium
catalyst
rhodium
platinum
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 - Fee Related
Application number
JP28286790A
Other languages
Japanese (ja)
Other versions
JPH04215845A (en
Inventor
保 中村
博文 新庄
幸治 横田
伸一 松本
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
Toyota Central R&D Labs Inc
Original Assignee
Toyota Motor Corp
Toyota Central R&D Labs Inc
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Priority to JP28286790A priority Critical patent/JP3251009B2/en
Publication of JPH04215845A publication Critical patent/JPH04215845A/en
Application granted granted Critical
Publication of JP3251009B2 publication Critical patent/JP3251009B2/en
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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は自動車等の内燃機関、石油ストーブあるいは
工場等から排出される炭化水素(HC)、一酸化炭素(C
O)ならびに窒素酸化物(NOx)を250℃以下の低温にお
いて効率良く除去する触媒およびその製造方法に関す
る。
DETAILED DESCRIPTION OF THE INVENTION (Industrial Application Field) The present invention relates to hydrocarbons (HC), carbon monoxide (C) discharged from internal combustion engines of automobiles, oil stoves or factories, etc.
The present invention relates to a catalyst for efficiently removing O) and nitrogen oxides (NO x ) at a low temperature of 250 ° C. or lower and a method for producing the same.

(従来技術) 最近、自然環境の維持が特に重視されつつあり、自動
車等の排気ガスの規制が強化される傾向にある。規制強
化の一貫として自動車の運転始動時(コールドスター
ト)の排気ガスからのNOx、HC、CO浄化の問題がある。
コールドスタート時の触媒層温度は、排気熱によって加
熱されるまでの間(約2分間)、300℃以下と低く、従
来の白金(Pt)、ロジウム(Rh)等の貴金属からなる触
媒金属、助触媒であるセリア(CeO2)等の希土類酸化物
とアルミナ(Al2O3)等の担体からなる自動車排気用三
元触媒では浄化活性を十分発揮する温度が300℃以上と
高いため排気熱によって触媒層が300℃以上に加熱され
るまでに排出される前記有害成分、特にHCは十分に浄化
されないのが現状である。そのため、コールドスター
ト時に触媒が活性を発揮する温度まで加熱するためのヒ
ータを内蔵した触媒コンバーターや、触媒の活性が生
じるまでの間、前記有害成分をゼオライト等を用いた吸
着トラッパーによってトラップする方法、COを酸化す
る能力を−70℃から有している金(Au)/酸化鉄(Fe2O
3)触媒を用いる方法等が考えられている。しかし、そ
れらはコスト面と技術的問題を有し、すなわちではヒ
ータ用バッテリーの容量の問題、すなわちヒータ加熱に
余分の電力が必要となって従来のバッテリーでは容量が
不足し大容量のバッテリーが必要となる。ではコール
ドスタート時に排出されるHCをすべて吸着するためには
非常に大きな吸着トラッパを設ける必要がある。では
HC浄化能が極めて劣っている点が大きな問題となってい
る。
(Prior Art) In recent years, maintenance of the natural environment has been given particular importance, and regulations on exhaust gas from automobiles and the like tend to be strengthened. As part of the tightening of regulations, there is a problem of purifying NO x , HC and CO from exhaust gas at the start of operation (cold start) of a vehicle.
The temperature of the catalyst layer at the time of cold start is as low as 300 ° C or less until it is heated by the exhaust heat (about 2 minutes). The catalyst layer is made of a conventional noble metal such as platinum (Pt) or rhodium (Rh). The three-way catalyst for automobile exhaust, which consists of rare earth oxides such as ceria (CeO 2 ) as a catalyst and a carrier such as alumina (Al 2 O 3 ), has a high purification temperature of 300 ° C or higher. At present, the harmful components, particularly HC, discharged until the catalyst layer is heated to 300 ° C. or more are not sufficiently purified. Therefore, at the time of a cold start, a catalyst converter having a built-in heater for heating to a temperature at which the catalyst exhibits activity, and a method of trapping the harmful component by an adsorption trapper using zeolite or the like until the activity of the catalyst occurs, Gold (Au) / iron oxide (Fe 2 O) having the ability to oxidize CO from -70 ° C
3 ) A method using a catalyst has been considered. However, they have cost and technical problems, that is, the capacity of the heater battery, that is, extra power is required for heating the heater, and the conventional battery is insufficient and needs a large capacity battery. Becomes Then, it is necessary to provide a very large adsorption trapper in order to adsorb all the HC discharged at the time of cold start. Then
A very poor HC purification ability is a major problem.

また石油ストーブ等においても、低温時に発生するHC
等の有害ガスの除去について同様な問題がある。
Also, in oil stoves, etc.,
There is a similar problem with the removal of harmful gases such as.

(発明の目的) 本発明は上記従来技術の欠点を解消するため、250℃
以下の低温域において、自動車の内燃機関等から排出さ
れる排気ガス中のNOx、HC、CO特にHCを効率良く除去可
能な新たな排気ガス浄化用の触媒およびその製造方法を
提供することを目的とする。
(Object of the Invention) The present invention solves the above-mentioned disadvantages of the prior art by using a 250 ° C.
In the following low temperature range, NO x in the exhaust gas discharged from an internal combustion engine of an automobile, HC, CO in particular to provide a catalyst and a manufacturing method thereof for efficiently removable new exhaust gas purifying HC Aim.

(第1発明の説明) 本第1発明は、コバルト、ニッケル、鉄、クロム、マ
ンガンのうちのいずれかの酸化物の一種以上と白金、ロ
ジウム、パラジウムの一種以上とからなり、前記酸化物
の少なくとも一種と前記白金およびロジウムならびにパ
ラジウムの少なくとも一種とが接触する界面で固溶し合
って250℃以下の温度において内燃機関などの排気ガス
中の炭化水素、一酸化炭素、窒素酸化物の浄化機能を生
じるように構成されていることを特徴とする排気ガス浄
化用触媒である。
(Description of the First Invention) The first invention comprises at least one oxide of cobalt, nickel, iron, chromium, and manganese and at least one of platinum, rhodium, and palladium. Purification function of hydrocarbons, carbon monoxide and nitrogen oxides in exhaust gas of internal combustion engines at a temperature of 250 ° C. or less at a temperature of 250 ° C. or lower by forming a solid solution at an interface where at least one of the platinum, rhodium and palladium contacts at least This is an exhaust gas purifying catalyst characterized by being configured to produce

本触媒によれば250℃以下という低温域においてHC、C
O、NOxを効率良く浄化できる。特に従来の触媒ではほと
んど浄化できなかったHCの浄化を可能とした。
According to this catalyst, HC, C
O, can be efficiently purify NO x. In particular, it enabled the purification of HC, which could hardly be purified with the conventional catalyst.

本触媒のかかる作用は明確ではないが以下のように考
えられる。
Although the action of the present catalyst is not clear, it is considered as follows.

従来の前記三元触媒は排気ガス中の有害成分であるC
O、HC、NOxを貴金属上に吸着し、以下に示すような反応
によって除去するものである。
The conventional three-way catalyst is a harmful component in exhaust gas, C
O, HC and NO x are adsorbed on the noble metal and removed by the following reaction.

CO+O2→CO2 …… NOx+H2→N2+H2O … NOx+CO→CO2+N2 … HC+O2→H2O+CO2 …… また助触媒であるCeO2に代表される希土類酸化物は担
体の熱安定性の向上、貴金属の高分散化の確保ととも
に、400℃以上において還元雰囲気下、すなわち排気ガ
ス中に酸素(O2)が不足していてもCeO2がO2を貴金属に
供給するいわゆるO2ストレージ能によりCOやHCの酸化を
進行させる働きを有する。しかし、250℃以下の低温で
はCOの貴金属への吸着が優先しておこり、O2、HC等の吸
着が妨げられHC、NOxの除去がほとんど行われなくな
り、また、CeO2のO2供給も250℃以下という低温ではほ
とんど行われずCeO2のO2ストレージ能に基づくHC等の浄
化も不可能であった。
CO + O 2 → CO 2 ··· NO x + H 2 → N 2 + H 2 O ··· NO x + CO → CO 2 + N 2 ··· HC + O 2 → H 2 O + CO 2 ··· Rare earth oxides such as CeO 2 which is a co-catalyst In addition to improving the thermal stability of the carrier and ensuring high dispersion of precious metals, CeO 2 converts O 2 to precious metals in a reducing atmosphere at 400 ° C or higher, that is, even if oxygen (O 2 ) is insufficient in exhaust gas. It has the function of advancing the oxidation of CO and HC by the so-called O 2 storage capacity to be supplied. However, in low-temperature 250 ° C. or less occurs in preference adsorption to the noble metal of CO, O 2, adsorption of the HC and the like is prevented HC, removal of NOx is not almost performed, also O 2 supply CeO 2 At a low temperature of 250 ° C. or less, it was hardly performed, and purification of HC and the like based on the O 2 storage capacity of CeO 2 was impossible.

本発明におけるコバルト、ニッケル、鉄、クロム、マ
ンガンのうちのいずれかの酸化物は前記CeO2とは異なり
250℃以下の低温でコバルト、ニッケル、鉄、クロム、
マンガンのうちのいずれかの金属自身が吸蔵しているO2
を吐き出して白金およびロジウムならびにパラジウムに
優先的に吸着したCOとの反応を促進せしめ、COをCO2
変えることができ、そのためO2、HCやNOxをも白金およ
びロジウムならびにパラジウムに吸着できるようにし、
HCやNOxの浄化を可能とするのである。
Cobalt in the present invention, nickel, iron, chromium, or an oxide of manganese is different from the CeO 2
Cobalt, nickel, iron, chromium,
O 2 occluded by any metal of manganese itself
The spit allowed promoting the reaction of CO were preferentially adsorbed on platinum and rhodium and palladium, CO can be changed to CO 2, can be adsorbed on the order O 2, HC, platinum and rhodium and palladium also NO x So that
Than it allows to purify the HC and NO x.

また、このように前記した反応〜が行われるため
その反応熱によって触媒自身の温度が上昇して触媒活性
も高められることになる。
In addition, since the above-mentioned reactions (1) to (4) are performed, the temperature of the catalyst itself increases due to the heat of the reaction, and the catalytic activity is also enhanced.

(第1発明のその他の発明の説明) 前記第1発明においてコバルト、ニッケル、鉄、クロ
ム、マンガンのうちのいずれかの金属の酸化物はCo
3O4、NiO、Fe2O3、Cr2O3、Nn2O3等が挙げられるが、こ
れらは例示にすぎない。これらの1種以上を用いる。こ
れらいずれかの金属酸化物の大きさは2000Å以下、ま
た、比表面積は0.2〜200m2/gで用いる。この範囲を超え
ると良好な浄化活性を発揮できない。望ましくは100Å
以下、50m2/g〜200m2/gが良い。
(Description of Other Inventions of First Invention) In the first invention, the oxide of any one of cobalt, nickel, iron, chromium, and manganese is Co.
Examples include 3 O 4 , NiO, Fe 2 O 3 , Cr 2 O 3 , Nn 2 O 3, etc., but these are only examples. One or more of these are used. Any of these metal oxides has a size of 2000 ° or less and a specific surface area of 0.2 to 200 m 2 / g. If it exceeds this range, good purification activity cannot be exhibited. Desirably 100Å
Below, 50m 2 / g~200m 2 / g is good.

貴金属としてRh、Pt、Pdの1種以上を用いる。その量
は前記金属酸化物に対し0.05〜10at%とする。0.05at%
以下だと浄化活性が発揮されず、逆に10at%以上だと前
記貴金属の量が多すぎて互いに凝集してしまい活性が低
下することになる。望ましくは1〜1.2at%が良い。前
記貴金属の粒径は500Å以下とする。
One or more of Rh, Pt, and Pd are used as the noble metal. The amount is 0.05 to 10 at% based on the metal oxide. 0.05at%
If the content is less than the above, the purification activity is not exhibited. Conversely, if the content is more than 10 at%, the amount of the noble metal is too large and agglomerates with each other to lower the activity. Desirably, the content is 1 to 1.2 at%. The particle size of the noble metal is 500 ° or less.

前記金属酸化物と前記貴金属とは均一に混合して用い
る。前記したように貴金属の表面に吸着したCOを金属酸
化物から吐き出されるO2によって酸化してCOを効率良く
貴金属表面から除去するためには貴金属と金属酸化物と
が密接して存在していることが必要なためである。また
これら両物質が接触する界面は固溶し合っている方が良
好な浄化特性を発揮する。
The metal oxide and the noble metal are uniformly mixed and used. As described above, in order to oxidize CO adsorbed on the surface of the noble metal by O 2 exhaled from the metal oxide and efficiently remove CO from the noble metal surface, the noble metal and the metal oxide are present in close contact It is necessary. In addition, the interface where these two substances come into contact with each other exhibits better purification characteristics when they are in solid solution.

本発明に係る触媒は以下に示す方法によって製造す
る。
The catalyst according to the present invention is produced by the following method.

従来公知の方法、前記金属の硝酸塩、有機金属塩又
は金属塩化物を熱分解したものに前述した貴金属のいず
れかの塩の水溶液を含浸して製造する方法、上記各種
金属塩を加水分解し、得られた水酸化物を焼成後、前述
したいずれかの貴金属を担持する方法、前述した金属
の塩と前述したいずれかの貴金属の塩とからなる混合溶
液から共沈して製造する方法のいずれかを用いてもよ
い。
A conventionally known method, a method of impregnating an aqueous solution of any of the above-described noble metal salts with a solution obtained by thermally decomposing the metal nitrate, organic metal salt or metal chloride, hydrolyzing the various metal salts, After the obtained hydroxide is calcined, any one of the method of supporting any of the above-mentioned noble metals and the method of co-precipitating from a mixed solution comprising the above-mentioned metal salt and any of the above-mentioned noble metal salts is used. May be used.

より具体的には、本発明の方法は、前述した金属の化
合物の沈澱と前記のいずれかの貴金属の化合物の沈澱と
の混合物を乾燥して粉末を作成し、その粉末を空気中で
加熱して焼成する製造方法である。
More specifically, the method of the present invention comprises the steps of drying a mixture of the precipitate of the above-mentioned metal compound and the precipitate of any of the above-mentioned noble metal compounds to form a powder, and heating the powder in air. This is a manufacturing method of firing.

あるいは、前述したいずれかの金属の化合物の粉末
に、前記のいずれかの貴金属の化合物の水溶液を含浸さ
せた後、前記粉末を空気中で加熱して焼成する製造方法
である。
Alternatively, a manufacturing method in which a powder of any one of the above-mentioned compounds of a metal is impregnated with an aqueous solution of any one of the above-mentioned compounds of a noble metal, and then the powder is heated in air to be fired.

前記の金属酸化物と前記貴金属とからなる触媒は、粉
状、ペレット状、ハニカム状等その形状・製造は問わな
い。また粉末状の触媒にアルミナゾルやシリカゾル、ジ
ルコニアゾル、チタニアゾル等のバインダーを添加し
て、所定の形状に成形したり、水を加えて、スラリー状
としてハニカム等の形状のアルミナ等の耐火性基体に塗
布してもよい。
The shape and production of the catalyst composed of the metal oxide and the noble metal are not limited, such as powder, pellet, and honeycomb. In addition, a binder such as alumina sol, silica sol, zirconia sol, titania sol, etc. is added to a powdered catalyst to form a predetermined shape, or water is added, and a slurry is formed on a refractory substrate such as alumina having a honeycomb shape in the form of a honeycomb. It may be applied.

実施例 本発明に係る触媒を製造し、該触媒について理論空燃
比のモデルガスを用い、NOx、CO、HCに対する浄化活性
評価を行った。また比較触媒についても同様の活性評価
を行った。
Example A catalyst according to the present invention was manufactured, and the purification activity of NO x , CO, and HC was evaluated for the catalyst using a model gas having a stoichiometric air-fuel ratio. Similar activity evaluation was also performed for the comparative catalyst.

実施例1 硝酸コバルト54gと硝酸パラジウム0.433gとを、イオ
ン交換水2に溶かしたもの(原子比Pd:Co=1:100)を
室温下で、分液ロートより約0.6m/sec速度で、炭酸ナ
トリウム50gをイオン交換水2に溶かしたアルカリ性
水溶液に滴下、撹拌する。この溶液を一時間放置した
後、ろ過、洗浄し、減圧乾燥する。そして得られた粉末
を空気中で350℃3時間焼成した。この焼成物を約2〜3
mmのサイコロ状に圧粉成型し、PdとCo3O4とからなる実
施例触媒No.1を得た。
Example 1 A solution obtained by dissolving 54 g of cobalt nitrate and 0.433 g of palladium nitrate in ion-exchanged water 2 (atomic ratio Pd: Co = 1: 100) at room temperature at a speed of about 0.6 m / sec from a separating funnel was obtained. 50 g of sodium carbonate is dropped into an alkaline aqueous solution dissolved in ion-exchanged water 2 and stirred. After leaving this solution for one hour, it is filtered, washed, and dried under reduced pressure. Then, the obtained powder was fired in air at 350 ° C. for 3 hours. About 2 to 3
The resultant was compacted into a die having a diameter of mm to obtain Example Catalyst No. 1 composed of Pd and Co 3 O 4 .

実施例2 実施例1の方法において、硝酸パラジウムの代わりに
ジニトロジアミノPtを用い(PtとCoとの原子比は1:100
と同一)アルカリ性水溶液として炭酸アンモニウムを用
いた以外は同一の条件でPtとCo3O4とからなる触媒No.2
を得た。
Example 2 In the method of Example 1, dinitrodiamino Pt was used instead of palladium nitrate (the atomic ratio of Pt to Co was 1: 100).
Catalyst No. 2 consisting of Pt and Co 3 O 4 under the same conditions except that ammonium carbonate was used as the alkaline aqueous solution
I got

実施例3 硝酸コバルト水溶液(50g/)を、炭酸ナトリウム水
溶液(50g/)に滴下して撹拌し、水酸化コバルトを沈
澱させた後、ろ過、洗浄し、さらに減圧乾燥し、その後
空気中で350℃3hr焼成して得た粉末に硝酸Pd水溶液をPd
含有量として1at%含浸し、その後空気中350℃で焼成し
た。この焼成物を2〜3mmのサイコロ状に圧粉成型し、P
dとCo3O4とからなる実施例触媒No.3を得た。
Example 3 An aqueous solution of cobalt nitrate (50 g /) was dropped into an aqueous solution of sodium carbonate (50 g /) and stirred to precipitate cobalt hydroxide, followed by filtration, washing, drying under reduced pressure, and drying in air under a pressure of 350 g. Pd nitric acid aqueous solution is added to the powder obtained by firing at
It was impregnated at a content of 1 at% and then fired at 350 ° C. in air. This calcined material is compacted into a die of 2-3 mm,
Example catalyst No. 3 consisting of d and Co 3 O 4 was obtained.

実施例4 実施例3の方法において硝酸Pdの代わりにジニトロジ
アミノPtを用いた以外は同一の条件でPtとCo3O4とから
なる実施例触媒No.4を得た。
Except for using dinitrodiamino Pt instead of Pd nitrate to give Example catalyst No.4 of Pt and Co 3 O 4 Metropolitan under the same conditions in the method of Example 4 Example 3.

実施例5 硝酸Coを600℃空気中5hr焼成し、熱分解させCo3O4
得る。このCo3O4粉末に硝酸Pd含有量3.5at%になるよう
に含浸し、その後空気中で350℃3hr焼成した。この焼成
物を2〜3mmのサイコロ状に圧粉成型し、PdとCo3O4とか
らなる実施例触媒No.5を得た。
Example 5 Co nitrate was calcined in air at 600 ° C. for 5 hours and thermally decomposed to obtain Co 3 O 4 . This Co 3 O 4 powder was impregnated so as to have a Pd nitrate content of 3.5 at%, and then fired in air at 350 ° C. for 3 hours. The calcined product was compacted into a die having a size of 2 to 3 mm to obtain Example Catalyst No. 5 composed of Pd and Co 3 O 4 .

実施例6 実施例5の方法において、硝酸Pdの代わりにジニトロ
ジアミノPtを用いた以外は同一の条件でPtとCo3O4とか
らなる実施例触媒No.6を得た。
Example 6 Example catalyst No. 6 consisting of Pt and Co 3 O 4 was obtained under the same conditions as in Example 5 except that dinitrodiamino Pt was used instead of Pd nitrate.

実施例7 実施例5の方法において、硝酸Coの代わりに硝酸Niを
用いた以外は同一の条件でPdとNiOとからなる実施例触
媒No.7を得た。
Example 7 Example catalyst No. 7 consisting of Pd and NiO was obtained under the same conditions as in Example 5 except that Ni nitrate was used instead of Co nitrate.

実施例8 実施例5の方法において、硝酸Coの代わりに硝酸第二
鉄を用いた以外は同一の条件で、PdとFe2O3とからなる
実施例触媒No.8を得た。
Example 8 Example catalyst No. 8 comprising Pd and Fe 2 O 3 was obtained under the same conditions as in Example 5 except that ferric nitrate was used instead of Co nitrate.

実施例9 実施例1の方法において、硝酸コバルト54gと硝酸パ
ラジウム0.433gの他に硝酸ニッケル18gを加え、そして
炭酸ナトリウム量を70gとした。それ以外は同一の条件
でPdとNiOならびにCo3O4とからなる実施例触媒No.9を得
た。
Example 9 In the method of Example 1, 18 g of nickel nitrate was added in addition to 54 g of cobalt nitrate and 0.433 g of palladium nitrate, and the amount of sodium carbonate was 70 g. Except for this, Example Catalyst No. 9 consisting of Pd, NiO, and Co 3 O 4 was obtained under the same conditions.

比較例1 比表面積約220m2/gLa含有のγ−Al2O3(La0.03mol/12
0g)粉末120g中にCeO2として0.3mol含有する様に硝酸Ce
を用い含浸させ650℃3hr大気中で焼成、その後Pt量とし
て1.5g含有する様にジニトロジアミノPt水溶液を用い、
含浸させ大気中で250℃、3hr仮焼した。その後、Rh量と
して0.3g含有する様に硝酸Rh水溶液を用いて含浸させ11
0℃一昼夜空気中乾燥させた。これを2〜3mm程度のサイ
コロ状に圧粉成型し、比較触媒No.C1を得た。本比較例
触媒は、通常自動車排気触媒に用いられているPt−Rh系
三元触媒である。
Comparative Example 1 γ-Al 2 O 3 having a specific surface area of about 220 m 2 / g La (La 0.03 mol / 12
0g) Ce nitrate so as to contain 0.3 mol as CeO 2 in 120 g of powder
And baked in the air at 650 ° C for 3 hours, then using an aqueous dinitrodiamino Pt solution to contain 1.5 g as Pt amount,
It was impregnated and calcined in the atmosphere at 250 ° C. for 3 hours. Thereafter, impregnation was performed using an aqueous solution of Rh nitrate so as to contain 0.3 g as an amount of Rh.
It was dried in air at 0 ° C. overnight. This was compacted into a die having a size of about 2 to 3 mm to obtain Comparative Catalyst No. C1. This comparative example catalyst is a Pt-Rh-based three-way catalyst usually used for an automobile exhaust catalyst.

比較例2 実施例1の方法において、硝酸パラジウムを加えない
でそれ以外は同一の条件でCo3O4のみからなる比較例触
媒No.C2を得た。
Comparative Example 2 A comparative example catalyst No. C2 consisting of only Co 3 O 4 was obtained in the same manner as in Example 1 except that palladium nitrate was not added and the other conditions were the same.

比較例3 比表面積約140m2/gのγ−Al2O3ペレット担体(2〜3m
mφ)を硝酸パラジウム水溶液に浸漬し、γ−Al2O3重量
に対しPd量が0.14wt%になる様に含浸し、空気中110
℃、5hr.乾燥し、600℃空気中3hr.焼成した。この焼成
物を約2〜3mmのサイコロ状に圧粉成型し、PdとAl2O3
からなる比較例触媒No.C3を得た。
Comparative Example 3 γ-Al 2 O 3 pellet carrier having a specific surface area of about 140 m 2 / g (2 to 3 m
mφ) in an aqueous solution of palladium nitrate, impregnated so that the Pd content is 0.14 wt% with respect to the weight of γ-Al 2 O 3 , and
℃, dried for 5 hours and calcined in air at 600 ° C for 3 hours. This calcined product was compacted into a die having a size of about 2 to 3 mm to obtain Comparative Example Catalyst No. C3 composed of Pd and Al 2 O 3 .

比較例4 比較例3の方法において、硝酸パラジウムの代わり
に、ジニトロジアミノPtを用いた以外は同一の条件でPt
とAl2O3とからなる比較例触媒No.C4を得た。
Comparative Example 4 Pt was obtained under the same conditions as in Comparative Example 3 except that dinitrodiamino Pt was used instead of palladium nitrate.
Comparative Example Catalyst No. C4 consisting of and Al 2 O 3 was obtained.

触媒活性評価 サイコロ状とした本実施例触媒No.1〜9および比較例
触媒No.C1〜C4を用い、第1表に示した理論空燃比のモ
デルガス中での50℃〜600℃における各成分(NO、CO、H
C)の昇温浄化特性を測定した。その結果のうち、実施
例触媒No.1を第1図に比較例触媒No.C1(従来の自動車
排気用三元触媒)を第2図に示した。
Evaluation of catalytic activity Using the catalysts of Example Nos. 1 to 9 and Comparative Example Nos. C1 to C4 in the form of dice, each of the catalysts at 50 ° C. to 600 ° C. in a model gas having a stoichiometric air-fuel ratio shown in Table 1 was used. Ingredients (NO, CO, H
The temperature raising purification characteristics of C) were measured. Of these results, Example Catalyst No. 1 is shown in FIG. 1 and Comparative Example Catalyst No. C1 (conventional three-way catalyst for automobile exhaust) is shown in FIG.

実施例触媒No.1は200℃においてCO、HC、NOを100%浄
化することができる。しかし、比較例触媒No.C1は、200
℃においても40〜80%程度低い浄化率であるにすぎな
い。
Example catalyst No. 1 can remove 100% of CO, HC and NO at 200 ° C. However, Comparative Example Catalyst No.
Even at ℃, the purification rate is only about 40 to 80% lower.

また、上記各触媒の測定結果をNO、CO、HCの50%浄化
率温度で整理して第2表に示した。
Table 2 summarizes the measurement results of the above catalysts at 50% purification rates of NO, CO, and HC.

実施例触媒No.1は、比較例触媒No.C1等に比べ(第1
図と第2図の比較並びに第2表での比較)、著しく低温
活性、特にHCに対し優れていることがわかる。
Example catalyst No. 1 was compared with comparative example catalyst No. C1 and the like (No. 1).
(Comparison between FIG. 2 and FIG. 2 and comparison in Table 2).

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

第1図は実施例触媒No.1、第2図は比較例触媒No.C1に
ついての温度に対する浄化率の関係を示した図である。
FIG. 1 is a diagram showing the relationship between the purification rate and the temperature for Example Catalyst No. 1 and FIG. 2 for Comparative Example Catalyst No. C1.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 横田 幸治 愛知県愛知郡長久手町大字長湫字横道41 番地の1 株式会社豊田中央研究所内 (72)発明者 松本 伸一 愛知県豊田市トヨタ町1番地 トヨタ自 動車株式会社内 審査官 繁田 えい子 (56)参考文献 特開 平1−224047(JP,A) 特開 昭63−178847(JP,A) 特開 昭62−152540(JP,A) 特開 昭62−176544(JP,A) 特開 昭63−185453(JP,A) 特開 昭58−189035(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01J 21/00 - 37/36 B01D 53/86 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Koji Yokota 41, Chukumi Yokomichi, Nagakute-cho, Aichi-gun, Aichi Prefecture Inside Toyota Central R & D Laboratories Co., Ltd. Examiner, Eiko Shigeta, Automobile Co., Ltd. (56) References JP-A 1-224047 (JP, A) JP-A 63-178847 (JP, A) JP-A 62-152540 (JP, A) JP 62-176544 (JP, A) JP-A-63-185453 (JP, A) JP-A-58-189035 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) B01J 21/00 -37/36 B01D 53/86

Claims (4)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】コバルト、ニッケル、鉄、クロム、マンガ
ンのうちのいずれかの酸化物の一種以上と白金、ロジウ
ム、パラジウムの一種以上とからなり、前記酸化物の少
なくとも一種と前記白金およびロジウムならびにパラジ
ウムの少なくとも一種とが接触する界面で固溶し合って
250℃以下の温度において内燃機関などの排気ガス中の
炭化水素、一酸化炭素、窒素酸化物の浄化機能を生じる
ように構成されていることを特徴とする排気ガス浄化用
触媒。
An oxide of at least one of cobalt, nickel, iron, chromium and manganese and at least one of platinum, rhodium and palladium, wherein at least one of said oxides and said platinum and rhodium; Solid solution at the interface where at least one of the palladium contacts
An exhaust gas purifying catalyst characterized in that it has a function of purifying hydrocarbons, carbon monoxide and nitrogen oxides in exhaust gas of an internal combustion engine or the like at a temperature of 250 ° C or less.
【請求項2】コバルト、ニッケル、鉄、クロム、マンガ
ンのうちのいずれかの酸化物の一種以上と白金、ロジウ
ム、パラジウムの一種以上とからなり、かつ前記酸化物
に対する前記白金およびロジウムならびにパラジウムの
少なくとも一種の量が0.05〜1.2at%であり、前記酸化
物の少なくとも一種と前記白金およびロジウムならびに
パラジウムの少なくとも一種とが接触する界面で固溶し
合って250℃以下の温度において内燃機関などの排気ガ
ス中の炭化水素、一酸化炭素、窒素酸化物の浄化機能を
生じるように構成されていることを特徴とする排気ガス
浄化用触媒。
2. An oxide comprising at least one oxide of any of cobalt, nickel, iron, chromium and manganese and at least one of platinum, rhodium and palladium, and said platinum, rhodium and palladium to said oxide. The amount of at least one is 0.05 to 1.2 at%, and at least one of the oxides and the platinum, rhodium, and at least one of palladium form a solid solution at an interface where they are in contact with each other and at a temperature of 250 ° C. An exhaust gas purifying catalyst characterized by having a function of purifying hydrocarbons, carbon monoxide and nitrogen oxides in exhaust gas.
【請求項3】コバルト、ニッケル、鉄、クロム、マンガ
ンのうちのいずれかの酸化物の一種以上と白金、ロジウ
ム、パラジウムの一種以上とからなる排気ガス浄化用触
媒の製造方法において、 コバルト、ニッケル、鉄、クロム、マンガンのうちのい
ずれかの化合物の沈澱と前記白金およびロジウムならび
にパラジウムの少なくとも一種の化合物の沈澱との混合
物を乾燥して粉末を作成し、その粉末を空気中で加熱し
て焼成することを特徴とする排気ガス浄化用触媒の製造
方法。
3. A method for producing an exhaust gas purifying catalyst comprising at least one of oxides selected from the group consisting of cobalt, nickel, iron, chromium and manganese and at least one of platinum, rhodium and palladium. A mixture of the precipitate of any of the compounds iron, chromium and manganese and the precipitate of at least one compound of platinum, rhodium and palladium is dried to form a powder, and the powder is heated in air to form a powder. A method for producing an exhaust gas purifying catalyst, characterized by firing.
【請求項4】コバルト、ニッケル、鉄、クロム、マンガ
ンのうちのいずれかの酸化物の一種以上と白金、ロジウ
ム、パラジウムの一種以上とからなる排気ガス浄化用触
媒の製造方法において、 コバルト、ニッケル、鉄、クロム、マンガンのうちのい
ずれかの化合物の粉末に、前記白金およびロジウムなら
びにパラジウムの少なくとも一種の化合物の水溶液を含
浸させた後、前記粉末を空気中で加熱して焼成すること
を特徴とする排気ガス浄化用触媒の製造方法。
4. A method for producing an exhaust gas purifying catalyst comprising at least one oxide selected from the group consisting of cobalt, nickel, iron, chromium and manganese, and at least one of platinum, rhodium and palladium. , Iron, chromium, powder of any one of the compounds of manganese, impregnated with an aqueous solution of at least one compound of the platinum, rhodium and palladium, the powder is heated in air and fired. A method for producing an exhaust gas purifying catalyst.
JP28286790A 1990-10-19 1990-10-19 Exhaust gas purification catalyst Expired - Fee Related JP3251009B2 (en)

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JP3251009B2 true JP3251009B2 (en) 2002-01-28

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Country Link
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