JPH0573461B2 - - Google Patents

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Publication number
JPH0573461B2
JPH0573461B2 JP61105863A JP10586386A JPH0573461B2 JP H0573461 B2 JPH0573461 B2 JP H0573461B2 JP 61105863 A JP61105863 A JP 61105863A JP 10586386 A JP10586386 A JP 10586386A JP H0573461 B2 JPH0573461 B2 JP H0573461B2
Authority
JP
Japan
Prior art keywords
alumina
catalyst
carrier
slurry
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 - Lifetime
Application number
JP61105863A
Other languages
Japanese (ja)
Other versions
JPS62262745A (en
Inventor
Takao Kawai
Ryoichiro Aihara
Masayasu Sato
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.)
KYATARA KOGYO KK
Original Assignee
KYATARA KOGYO KK
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 KYATARA KOGYO KK filed Critical KYATARA KOGYO KK
Priority to JP61105863A priority Critical patent/JPS62262745A/en
Publication of JPS62262745A publication Critical patent/JPS62262745A/en
Publication of JPH0573461B2 publication Critical patent/JPH0573461B2/ja
Granted legal-status Critical Current

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

[産業上の利用分野] この発明は、炭化水素(HC)、一酸化炭素
(CO)および窒化酸化物(NOX)の無害化に使
用するための触媒担体に関し、特に自動車排気ガ
スおよび固定型エンジン排気ガスの浄化に使用す
る触媒担体に関する。 [従来の技術] 一体型構造担体(モノリス担体)には、材質、
形状、製法につき各種あるが、一般的にはコーニ
ング社製、日本碍子株式会社製のコーデイエライ
ト質、角型セルのモノリス担体が多く使用されて
いる。このコーデイエライト質モノリス担体は、
比表面積が約1m2/gと非常に小さいので、貴金
属のような触媒金属を担体しても、担体表面上へ
分散させることができない。その結果、初期性
能、耐久性能がともに劣る触媒しか得られず、こ
のまま担体として使用するには実用性がない。そ
こで従来、上記欠点を解決するために、モノリス
担体に、活性アルミナ被膜を形成せしめ、比表面
積を増大させて触媒金属の分散性を向上させ、性
能を良好にすることが行なわれている。 従来、このアルミナ被膜に使用される活性アル
ミナは、特公昭56−27295号公報にみるごとく、
約50m2/g以上の比表面積を有するアルミナが使
用されており、比表面積50m2/g未満であるα、
θ−アルミナについて積極的に利用された例は少
ない。特開昭54−148187号公報において、δ−ア
ルミナが主体でx、γ、κ、θ、ρ−アルミナが
一部という記述にみられる如く、活性アルミナの
一部にθ−アルミナが混在しても良いとする見解
はある。 [発明が解決しようとする問題点] 従来の自動車排ガス浄化用触媒に対する要求性
能は、触媒入口ガス温度の上限が800℃前後とな
つていたことから、800℃までの熱耐久性がある
ことであつた。しかしながら最近の触媒取付け位
置の排気管上流部への移動や高速走行での使用を
重視することから、触媒入口ガス温度の上限が上
昇して900℃前後となつており、触媒温度は1000
℃程度になつていると考えられる。その結果、従
来それほど重視されていなかつた高温耐久性が最
近とくに問題視されるようになつた。従つて従来
技術による触媒では高温耐久性が不十分である。
この理由を推測するに、特公昭56−27295号公報
や特開昭54−148187号公報に示される活性アルミ
ナ種では、1000℃の高温下では結晶が変態を起こ
し、新品状態では、触媒金属が高分散に担持され
ていたにもかかわらず、結果的に触媒金属のシン
タリングが助長されることにより触媒性能が低下
するものと考えられる。 また耐久性試験を実施してその耐久触媒を調査
すると、排ガス流路方向、上流側半分の触媒の性
能の劣化が、残り半分の触媒の性能の劣化に比べ
て大きいことが判明した。さらに、それぞれの比
表面積を測定すると、上流側半分の触媒の比表面
積の低下が著しく、性能劣化の原因は上流側半分
で高温状態が生じたためと考えられる。 従つて従来の触媒の問題点は、高温耐久性に乏
しく、特に上流側半分の高温耐久性が弱いという
ことがいえる。 [問題点を解決するための手段] 本発明者らは上記従来技術の問題点を解決すべ
く鋭意研究を行なつた結果、従来の触媒に比べ、
高温耐久性のすぐれた排ガス浄化用触媒となり得
る触媒担体を提供することに成功した。 すなわち、この発明の排ガス浄化用触媒担体
は、触媒金属を担持するためのハニカムモノリス
基材上の活性アルミナコーテイング層の排ガス流
路方向上流側が、α−アルミナおよびθ−アルミ
ナを含む活性アルミナコーテイング層からなり、
下流側が、δ−アルミナおよびγ−アルミナから
選ばれた少くとも一種からなることを特徴とする
ものである。 この発明においては、基材として用いるモノリ
ス担体は、コージエライト、ムライト等であり、
基材の形態は、三角、四角、波形のセル構造のも
のがよい。 なお、本発明の触媒担体に担持される触媒金属
としては、白金、パラジウムおよびロジウムのう
ちの少くとも一種を用いるのが好ましい。 [作用] 本発明の触媒担体は、使用中に下流側に比べて
高温状態となる上流側に、熱による結晶変態が起
こりにくいα−アルミナおよびθ−アルミナを含
む活性アルミナをコーテイング層として施してあ
り、したがつて、その上に担持してある触媒金属
の高温状態下での熱によるシンタリングが起こり
にくく、その結果として高温耐久性にすぐれた触
媒を提供することができる。 また、下流側は上流側に比べ高温になりにく
く、しかも比表面積が50m2/g以上のδ−アルミ
ナおよびγ−アルミナをコーテイングしてあるた
め、担持してある触媒金属の分散性が良好であ
り、耐久性のすぐれた触媒を提供することができ
る。 [実施例] 実施例 1 日産化学社製アルミナゾル(商品名AS−200)
700g(アルミナ分70g)と、硝酸アルミニウム
9水和物60gと、イオン交換水200gと、比表面
積が100m2/gでX線回折でδおよびγを示すア
ルミナを1100℃で3時間焼成したアルミナ粉末
(比表面積が20m2/gを示し、X線回折を行うと
θ−およびα−アルミナを検出した)1000gとを
3時間混合撹拌してスラリーを調製した。 このスラリーをAスラリーとした。 次にアルミナ粉末として、比表面積100m2/g
でX線回折でδおよびγを示すアルミナを用い、
かつイオン交換水350gを用いた以外は、上記A
スラリーと同様の組成のものを3時間混合撹拌し
てスラリーを調製し、このスラリーをBスラリー
とした。 毎平方インチ300個のセルを有する円筒形状の
コーデイエライト製モノリス担体(日本碍子株式
会社製、直径93mm、長さ100mm、体積0.679)を
水中に浸し、十分に吸水させたのち取り出し、セ
ル内に残つた水を空気流(5Kg/mm2の圧力)で吹
き払つた。先に調製したAスラリー中にこの吸水
させた担体の半分(上流側部分)を浸漬し取り出
し、スラリーの付着していない反対側から担体半
分に付着したセル内の過剰のスラリーを空気流を
用いて吹き払つた。このようにしてAスラリーを
付着した担体を110℃で1時間乾燥後、電気炉を
用い空気中700℃で1時間焼成して、モノリス担
体半分(上流側部分)に43gのAアルミナ被膜を
形成させた。 またBスラリー中に、アルミナ被膜が形成して
いないモノリス担体の半分(下流側部分)だけ浸
漬し取り出して、Bスラリーが付着していない反
対側からセル内の過剰のスラリーを空気流を用い
て吹き払い、この担体を110℃で1時間乾燥後、
電気炉を用い空気中700℃で1時間焼成して43g
のBアルミナ被膜をモノリス担体半分(下流側部
分)に形成し、総計で86gのA被膜とB被膜とか
らなるアルミナコーテイング層を含む触媒担体を
得た。この触媒担体のアルミナコーテイング層を
けずり落しX線回折により化合物の同定分析を行
うと上流側部分からはθ−アルミナとα−アルミ
ナとが検出された。さらに下流側部分からはδ−
アルミナとγ−アルミナとが検出された。 次にこの触媒担体の半分を白金アンミン水溶液
中に浸漬し、触媒担体に触媒金属の白金を吸着さ
せたのち、残りの半分も同様に白金を吸着させて
さらに水洗し、引きつづき同様に、半分ずつ塩化
ロジウム水溶液中に浸漬して、触媒担体に触媒金
属のロジウムを担持させ、ついで100℃で乾燥後、
500℃で30分間焼成して排ガス浄化用触媒を得た。
この触媒に担持された貴金属担持量の化学分析を
行つたところ、白金の担持量は1.0g/−触媒
およびロジウムの担持量は0.1g/−触媒であ
つた。 実施例 2 実施例1と同様に、モノリス担体の上流側部分
にAスラリーを用いてコーテイング被膜を形成さ
せ、下流側部分には次のように調製したCスラリ
ーを用いて被膜を形成させた。 Cスラリーは、アルミナ粉末として比表面積が
130m2/gで、X線回折でγ−アルミナを示す活
性アルミナを用い、かつイオン交換水350gを用
いた以外は、上記Aスラリーと同様の組成のもの
を混合撹拌して調製したものである。この触媒担
体のアルミナコーテイング層をけずり落し、X線
回折により化合物の同定分析を行うと、上流側部
分からはθ−およびα−アルミナ、また下流側部
分からはγ−アルミナが検出された。 次に実施例1と同様にこのコーテイング担体に
白金を1.0g/−触媒およびロジウムを0.1g/
−触媒担持し、排ガス浄化用触媒を得た。 実施例 3 実施例1と同様に、モノリス担体の上流側部分
にAスラリーを用いてコーテイング被膜を形成さ
せ、下流側部分には次の様に調製したDスラリー
を用いてコーテイング被膜を形成させた。 Dスラリーは、アルミナ粉末としては比表面積
が50m2/gで、X線回折でδ−とθ−アルミナを
示す活性アルミナを用い、かつイオン交換水300
gを用いた以外は、上記Aスラリーと同様の組成
のものを混合撹拌して調製したものである。 この触媒担体のアルミナコーテイング層をけず
り落し、X線回折により同定すると、上流側部分
からは、θ−およびα−アルミナ、また下流側部
分からは、δ−およびθ−アルミナが検出され
た。 次に、実施例1と同様にこの触媒担体に、白金
1g/−触媒およびロジウム0.1g/−触媒
を担持し、排ガス浄化用触媒を得た。 比較例 1 実施例1、2および3で用いたAスラリーをモ
ノリス担体全部にコーテイングし、乾燥、焼成し
て86gの被膜を形成させた。このコーテイング層
をけずり落して、X線回折により同定するとαと
θのアルミナが検出された。このコーテイング担
体に実施例1同様に白金を1.0g/−触媒およ
びロジウムを0.1g/−触媒担持して排ガス浄
化用触媒を得た。 比較例 2 実施例1で用いたBスラリーをモノリス担体全
部にコーテイングし、乾燥、焼成して86gの被膜
を形成させた。このコーテイング層をけずり落し
て、X線回折により同定するとδとγのアルミナ
が検出された。このコーテイング担体に実施例1
と同様に白金を1.0g/−触媒およびロジウム
を0.1g/−触媒担持して排ガス浄化用触媒を
得た。 比較例 3 実施例2で用いたCスラリーをモノリス担体全
部にコーテイングし、乾燥・焼成して86gの被膜
を形成させた。このコーテイング層をけずり落し
て、X線回折により同定するとγ−アルミナが検
出された。このコーテイング担体に実施例1と同
様に白金を1.0g/−触媒およびロジウムを0.1
g/−触媒担体して排ガス浄化用触媒を得た。
第1表に、実施例1〜3および比較例1〜3のア
ルミナの形態をまとめて示した。
[Industrial Application Field] The present invention relates to a catalyst carrier for use in detoxifying hydrocarbons (HC), carbon monoxide (CO), and nitrided oxides ( NOx ), and particularly for use in automobile exhaust gas and stationary The present invention relates to a catalyst carrier used for purifying engine exhaust gas. [Prior art] An integrated structure carrier (monolith carrier) has various materials,
Although there are various shapes and manufacturing methods, generally cordierite and square cell monolith carriers manufactured by Corning and Nippon Insulators are often used. This cordierite monolithic support is
Since the specific surface area is very small, about 1 m 2 /g, even if a catalytic metal such as a noble metal is supported, it cannot be dispersed on the surface of the support. As a result, catalysts with poor initial performance and poor durability are obtained, and are not practical for use as a carrier as they are. Conventionally, in order to solve the above-mentioned drawbacks, an active alumina coating has been formed on a monolithic carrier to increase the specific surface area, improve the dispersibility of the catalyst metal, and improve the performance. Conventionally, the activated alumina used for this alumina coating is as shown in Japanese Patent Publication No. 56-27295.
Alumina having a specific surface area of about 50 m 2 /g or more is used, and α has a specific surface area of less than 50 m 2 /g,
There are few examples of active use of θ-alumina. In JP-A-54-148187, as seen in the description that δ-alumina is the main component and x, γ, κ, θ, and ρ-alumina are a part, θ-alumina is mixed in a part of the activated alumina. There is a view that it is also good. [Problems to be solved by the invention] The required performance for conventional catalysts for purifying automobile exhaust gas is that the upper limit of the catalyst inlet gas temperature is around 800℃, so it is necessary to have thermal durability up to 800℃. It was hot. However, in recent years, the catalyst installation position has been moved to the upstream part of the exhaust pipe and emphasis is placed on use at high speeds, so the upper limit of the catalyst inlet gas temperature has increased to around 900℃, and the catalyst temperature has increased to around 1000℃.
It is thought that the temperature is around ℃. As a result, high-temperature durability, which had not been given much importance in the past, has recently come to be viewed as a particular problem. Therefore, catalysts according to the prior art have insufficient high temperature durability.
The reason for this is that in the activated alumina species shown in Japanese Patent Publication No. 56-27295 and Japanese Patent Application Laid-open No. 54-148187, the crystals undergo transformation at a high temperature of 1000°C, and when new, the catalytic metal is Although the catalyst metal was supported in a highly dispersed manner, it is thought that sintering of the catalyst metal was promoted as a result, resulting in a decrease in catalyst performance. Furthermore, when durability tests were conducted to investigate the durability of the catalyst, it was found that the performance of the catalyst in the upstream half of the catalyst in the exhaust gas flow direction deteriorated to a greater extent than the performance of the remaining half of the catalyst. Furthermore, when the specific surface area of each catalyst was measured, the specific surface area of the upstream half of the catalyst was significantly reduced, and the reason for the performance deterioration is thought to be the high temperature that occurred in the upstream half. Therefore, the problem with conventional catalysts is that they lack high-temperature durability, particularly in the upstream half. [Means for Solving the Problems] The present inventors have conducted intensive research to solve the problems of the above-mentioned conventional techniques, and as a result, compared to conventional catalysts,
We have succeeded in providing a catalyst carrier that can be used as an exhaust gas purification catalyst with excellent high-temperature durability. That is, in the exhaust gas purifying catalyst carrier of the present invention, the activated alumina coating layer on the honeycomb monolith base material for supporting catalyst metal has an activated alumina coating layer containing α-alumina and θ-alumina on the upstream side in the exhaust gas flow direction. Consisting of
The downstream side is characterized by comprising at least one type selected from δ-alumina and γ-alumina. In this invention, the monolith carrier used as the base material is cordierite, mullite, etc.
The base material preferably has a triangular, square, or wavy cell structure. In addition, as the catalyst metal supported on the catalyst carrier of the present invention, it is preferable to use at least one of platinum, palladium, and rhodium. [Function] The catalyst carrier of the present invention has activated alumina containing α-alumina and θ-alumina, which is less susceptible to crystal transformation due to heat, applied as a coating layer on the upstream side, which is in a higher temperature state than the downstream side during use. Therefore, sintering of the catalyst metal supported thereon by heat under high-temperature conditions is less likely to occur, and as a result, a catalyst with excellent high-temperature durability can be provided. In addition, the downstream side is less prone to high temperatures compared to the upstream side, and is coated with δ-alumina and γ-alumina with a specific surface area of 50 m 2 /g or more, so the supported catalyst metal has good dispersibility. It can provide a highly durable catalyst. [Example] Example 1 Alumina sol manufactured by Nissan Chemical Co., Ltd. (trade name AS-200)
700g (alumina content 70g), 60g of aluminum nitrate nonahydrate, 200g of ion-exchanged water, and alumina with a specific surface area of 100m 2 /g and showing δ and γ in X-ray diffraction were calcined at 1100℃ for 3 hours. A slurry was prepared by mixing and stirring 1000 g of powder (having a specific surface area of 20 m 2 /g and detecting θ- and α-alumina by X-ray diffraction) for 3 hours. This slurry was designated as A slurry. Next, as alumina powder, the specific surface area is 100m 2 /g
Using alumina that shows δ and γ in X-ray diffraction,
The above A except that 350g of ion-exchanged water was used.
A slurry having the same composition as the slurry was mixed and stirred for 3 hours to prepare a slurry, and this slurry was designated as Slurry B. A cylindrical monolith carrier made of cordierite (manufactured by Nippon Insulators Co., Ltd., diameter 93 mm, length 100 mm, volume 0.679) having 300 cells per square inch is immersed in water, and after absorbing sufficient water, it is taken out and placed inside the cells. The remaining water was blown away with a stream of air (pressure of 5 kg/mm 2 ). Half of this water-absorbed carrier (upstream part) is immersed in the previously prepared slurry A and taken out, and the excess slurry in the cells that has adhered to the half of the carrier is removed from the opposite side to which the slurry is not attached using an air flow. I blew it away. After drying the carrier to which A slurry was attached in this way at 110°C for 1 hour, it was fired in air at 700°C for 1 hour using an electric furnace to form a 43g A alumina coating on half of the monolithic carrier (upstream part). I let it happen. In addition, only half of the monolith carrier (the downstream part) on which the alumina coating is not formed is immersed in the B slurry, and taken out, and the excess slurry in the cell is removed from the opposite side to which the B slurry is not attached using an air flow. After blowing off and drying this carrier at 110℃ for 1 hour,
Baked in air at 700℃ for 1 hour using an electric furnace to yield 43g.
A B alumina coating was formed on half of the monolithic carrier (downstream portion) to obtain a catalyst carrier containing an alumina coating layer consisting of the A coating and the B coating, weighing a total of 86 g. When the alumina coating layer of this catalyst carrier was scraped off and the compounds were identified and analyzed by X-ray diffraction, θ-alumina and α-alumina were detected from the upstream portion. Furthermore, from the downstream part, δ−
Alumina and γ-alumina were detected. Next, half of this catalyst carrier is immersed in a platinum ammine aqueous solution to adsorb platinum, the catalytic metal, on the catalyst carrier.The other half is also adsorbed with platinum and further washed with water. The catalyst carrier was immersed in a rhodium chloride aqueous solution to support the catalyst metal rhodium, and then dried at 100°C.
An exhaust gas purifying catalyst was obtained by firing at 500°C for 30 minutes.
Chemical analysis of the amount of noble metal supported on this catalyst revealed that the amount of platinum supported was 1.0 g/-catalyst and the amount of rhodium supported was 0.1 g/-catalyst. Example 2 Similarly to Example 1, a coating film was formed on the upstream portion of the monolithic carrier using slurry A, and a coating film was formed on the downstream portion using slurry C prepared as follows. C slurry has a specific surface area as alumina powder.
It was prepared by mixing and stirring a slurry having the same composition as the slurry A above, except that activated alumina having a size of 130 m 2 /g and showing γ-alumina in X-ray diffraction was used, and 350 g of ion-exchanged water was used. . When the alumina coating layer of this catalyst carrier was scraped off and the compounds were identified and analyzed by X-ray diffraction, θ- and α-alumina were detected from the upstream portion, and γ-alumina was detected from the downstream portion. Next, as in Example 1, 1.0 g/- of platinum and 0.1 g/- of rhodium were added to the coated carrier.
- A catalyst-supported catalyst for exhaust gas purification was obtained. Example 3 Similarly to Example 1, a coating film was formed on the upstream part of the monolithic carrier using slurry A, and a coating film was formed on the downstream part using slurry D prepared as follows. . Slurry D uses activated alumina that has a specific surface area of 50 m 2 /g as alumina powder and shows δ- and θ-alumina in X-ray diffraction, and contains 300 m2 of ion-exchanged water.
This slurry was prepared by mixing and stirring a slurry having the same composition as the above slurry A except that g was used. When the alumina coating layer of this catalyst carrier was scraped off and identified by X-ray diffraction, θ- and α-alumina were detected from the upstream portion, and δ- and θ-alumina were detected from the downstream portion. Next, in the same manner as in Example 1, 1 g/- of platinum and 0.1 g/- of rhodium were supported on this catalyst carrier to obtain an exhaust gas purifying catalyst. Comparative Example 1 Slurry A used in Examples 1, 2 and 3 was coated on the entire monolithic carrier, dried and fired to form a film of 86 g. When this coating layer was scraped off and identified by X-ray diffraction, α and θ alumina were detected. As in Example 1, 1.0 g/- of platinum and 0.1 g/- of rhodium were supported on this coated carrier to obtain an exhaust gas purifying catalyst. Comparative Example 2 The entire monolithic carrier was coated with the B slurry used in Example 1, dried and fired to form a coating of 86 g. When this coating layer was scraped off and identified by X-ray diffraction, δ and γ alumina were detected. Example 1
In the same manner as above, 1.0 g/- of platinum and 0.1 g/- of rhodium were supported on the catalyst to obtain an exhaust gas purifying catalyst. Comparative Example 3 The entire monolithic carrier was coated with the C slurry used in Example 2, dried and fired to form a coating of 86 g. When this coating layer was scraped off and identified by X-ray diffraction, γ-alumina was detected. As in Example 1, 1.0 g of platinum/catalyst and 0.1 g of rhodium were added to this coated carrier.
g/- catalyst carrier to obtain an exhaust gas purifying catalyst.
Table 1 shows the forms of alumina in Examples 1 to 3 and Comparative Examples 1 to 3.

【表】 実施例4および比較例4 実施例1および比較例1で得られた触媒担体
に、それぞれ白金アンミン水溶液、塩化パラジウ
ム水溶液および塩化ロジウム水溶液を使用して、
実施例1と同様の方法で、白金0.5g/−触媒、
パラジウム0.5g/−触媒およびロジウム0.1
g/−触媒を担持して排ガス浄化用触媒を得
た。 実施例5および比較例5 実施例1および比較例1で得た触媒担体に、そ
れぞれ塩化パラジウム水溶液および塩化ロジウム
水溶液を使用して、実施例1と同様の方法で、パ
ラジウム1.0g/−触媒およびロジウム0.1g/
−触媒を担持して排ガス浄化用触媒を得た。 触媒耐久性能評価試験結果 耐久試験条件は、排気量3800c.c.のエンジンに
て、回転数3300rpm、ブースト−100mmHg、触媒
入ガス温度890℃、空燃比(A/F)14.5で50時
間触媒を排気ガスにさらすという条件である。こ
のようにして、耐久した触媒の性能評価は、排気
量1600c.c.のエンジンにて回転数2600rpm、ブース
ト−360mmHg、触媒入ガス温度460℃、A/F14.5
なる条件で耐久性後の触媒に排気ガスを通じ、炭
化水素(HC)、一酸化炭素(CO)、窒素酸化物
(NOX)に対する浄化率を算出することにより行
つた。これらの結果を第2表に示した。
[Table] Example 4 and Comparative Example 4 Platinum ammine aqueous solution, palladium chloride aqueous solution and rhodium chloride aqueous solution were used on the catalyst supports obtained in Example 1 and Comparative Example 1, respectively.
In the same manner as in Example 1, platinum 0.5g/-catalyst,
Palladium 0.5g/-catalyst and rhodium 0.1
A catalyst for exhaust gas purification was obtained by supporting the catalyst. Example 5 and Comparative Example 5 Palladium 1.0 g/-catalyst and Rhodium 0.1g/
- A catalyst for exhaust gas purification was obtained by supporting the catalyst. Catalyst durability performance evaluation test results The durability test conditions were an engine with a displacement of 3800 c.c., a rotation speed of 3300 rpm, a boost of -100 mmHg, a catalyst inlet gas temperature of 890°C, and an air-fuel ratio (A/F) of 14.5 for 50 hours. The condition is that it is exposed to exhaust gas. In this way, the performance of the durable catalyst was evaluated using an engine with a displacement of 1600 c.c. at a rotation speed of 2600 rpm, a boost of -360 mmHg, a catalyst inlet gas temperature of 460°C, and an A/F of 14.5.
Exhaust gas was passed through the catalyst after durability under the following conditions, and the purification rate for hydrocarbons (HC), carbon monoxide (CO), and nitrogen oxides (NO x ) was calculated. These results are shown in Table 2.

【表】 [発明の効果] 以上の結果から明白なように、本発明の触媒担
体は、同一の触媒金属を担持した従来の触媒担体
と比較して、高温耐久性において、非常にすぐれ
た触媒性能を発揮させることができる。
[Table] [Effects of the Invention] As is clear from the above results, the catalyst carrier of the present invention is a catalyst with extremely superior high-temperature durability compared to conventional catalyst carriers that support the same catalyst metal. performance can be demonstrated.

Claims (1)

【特許請求の範囲】[Claims] 1 ハニカムモノリス基材に活性アルミナのコー
テイング層を施してなる排ガス浄化用触媒担体に
おいて、排ガス流路方向に対し、上流側の活性ア
ルミナのコーテイング層がα−アルミナおよびθ
−アルミナを含む活性アルミナからなるコーテイ
ング層であり、下流側の活性アルミナのコーテイ
ング層がδ−アルミナおよびγ−アルミナから選
ばれた少くとも一種を含む活性アルミナからなる
コーテイング層であることを特徴とする排ガス浄
化用触媒担体。
1 In a catalyst carrier for exhaust gas purification formed by applying a coating layer of activated alumina to a honeycomb monolith base material, the coating layer of activated alumina on the upstream side in the direction of the exhaust gas flow path contains α-alumina and θ-alumina.
- a coating layer made of activated alumina containing alumina, characterized in that the coating layer of activated alumina on the downstream side is a coating layer made of activated alumina containing at least one selected from δ-alumina and γ-alumina; Catalyst carrier for exhaust gas purification.
JP61105863A 1986-05-09 1986-05-09 Catalyst carrier for purifying exhaust gas Granted JPS62262745A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61105863A JPS62262745A (en) 1986-05-09 1986-05-09 Catalyst carrier for purifying exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61105863A JPS62262745A (en) 1986-05-09 1986-05-09 Catalyst carrier for purifying exhaust gas

Publications (2)

Publication Number Publication Date
JPS62262745A JPS62262745A (en) 1987-11-14
JPH0573461B2 true JPH0573461B2 (en) 1993-10-14

Family

ID=14418811

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61105863A Granted JPS62262745A (en) 1986-05-09 1986-05-09 Catalyst carrier for purifying exhaust gas

Country Status (1)

Country Link
JP (1) JPS62262745A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5010051A (en) * 1989-11-08 1991-04-23 Engelhard Corporation Staged three-way conversion catalyst and method of using the same
JP4311918B2 (en) 2002-07-09 2009-08-12 ダイハツ工業株式会社 Method for producing perovskite complex oxide
AU2003281203A1 (en) 2002-07-09 2004-01-23 Cataler Corporation Catalyst for clarifying exhaust gas
JP4844790B2 (en) * 2004-02-27 2011-12-28 株式会社豊田中央研究所 Hydrogen production catalyst

Also Published As

Publication number Publication date
JPS62262745A (en) 1987-11-14

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