JPH04293546A - Exhaust gas purifying catalyst - Google Patents

Exhaust gas purifying catalyst

Info

Publication number
JPH04293546A
JPH04293546A JP3058640A JP5864091A JPH04293546A JP H04293546 A JPH04293546 A JP H04293546A JP 3058640 A JP3058640 A JP 3058640A JP 5864091 A JP5864091 A JP 5864091A JP H04293546 A JPH04293546 A JP H04293546A
Authority
JP
Japan
Prior art keywords
oxide
honeycomb carrier
exhaust gas
cerium oxide
cerium
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.)
Granted
Application number
JP3058640A
Other languages
Japanese (ja)
Other versions
JP3099392B2 (en
Inventor
Ikuo Matsumoto
松本 郁夫
Kenji Tabata
研二 田畑
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.)
Panasonic Holdings Corp
Original Assignee
Matsushita Electric Industrial 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 Matsushita Electric Industrial Co Ltd filed Critical Matsushita Electric Industrial Co Ltd
Priority to JP03058640A priority Critical patent/JP3099392B2/en
Publication of JPH04293546A publication Critical patent/JPH04293546A/en
Application granted granted Critical
Publication of JP3099392B2 publication Critical patent/JP3099392B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PURPOSE:To obtain a catalyst composition generating no catalytic activity even in a reducing atmosphere at high temp. 200 deg.C or higher and excellent in durability. CONSTITUTION:Cerium oxide is preliminarily supported on a honeycomb carrier and a composition based on a fine powder of a perovskite multicomponent oxide, a fine powder of zirconia, iron oxide and at least one or more kinds of a noble metal element is applied to the cerium oxide layer to obtain a catalyst composition excellent in durability shown by Fig. 1.

Description

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

【0001】0001

【産業上の利用分野】本発明は排ガス浄化触媒に関し、
特に石油やガスを燃料とした各種の家庭用や工業用燃焼
器及び自動車等の排ガスをクリーンに浄化させる排ガス
浄化触媒に関する。
[Industrial Application Field] The present invention relates to an exhaust gas purification catalyst.
In particular, the present invention relates to an exhaust gas purification catalyst that cleanly purifies exhaust gas from various household and industrial combustors and automobiles using oil or gas as fuel.

【0002】0002

【従来の技術】従来この種の排ガス浄化触媒の触媒組成
物としてはセラミックス担体上に酸化セリウムを担持さ
せ、その上からペロブスカイト複合酸化物微粉末を担持
させ、さらに貴金属を担持させたもの(特開昭01−3
04046)や、酸化セリウムとペロブスカイト複合酸
化物粉末の担持順序を逆にしたもの(特開昭01−30
4048)があった。
[Prior Art] Conventionally, the catalyst composition for this type of exhaust gas purification catalyst is one in which cerium oxide is supported on a ceramic carrier, fine perovskite composite oxide powder is supported on the ceramic carrier, and a noble metal is further supported on the ceramic carrier. Kaisho 01-3
04046), and one in which the supporting order of cerium oxide and perovskite composite oxide powder is reversed (Japanese Unexamined Patent Publication No. 1987-30
4048).

【0003】0003

【発明が解決しようとする課題】しかしながら上記従来
の触媒組成は200℃以上の高温で還元性雰囲気中で長
時間使用するとパラジウムなどの貴金属が粒成長を起し
たり、ペロブスカイト型複合酸化物中に拡散したりして
触媒活性が次第に低下する等耐久性が劣るという課題が
あった。
[Problems to be Solved by the Invention] However, when the above-mentioned conventional catalyst composition is used for a long time in a reducing atmosphere at a high temperature of 200°C or higher, noble metals such as palladium may cause grain growth, and the perovskite type composite oxide may There was a problem that the durability was poor, such as the catalytic activity gradually decreasing due to diffusion.

【0004】本発明は上記課題を解決するもので、耐久
性の優れた触媒組成物を主体とする排ガス浄化触媒を提
供することを目的とする。
[0004] The present invention solves the above problems, and aims to provide an exhaust gas purification catalyst mainly composed of a catalyst composition having excellent durability.

【0005】[0005]

【課題を解決するための手段】上記目的を達成するため
本発明の排ガス浄化触媒は、コーディエライト質を主体
とする耐熱性セラミックスのハニカム担体に酸化セリウ
ムをさせ、さらにその上からABO3 の基本構造を有
するペロブスカイト複合酸化物の微粉末、ジルコニア微
粉末、酸化鉄、及び白金、パラジウム、ロジウムなどの
貴金属元素の中の1種類以上の元素と、アルミナゾル、
硝酸アルミニウムとを焼成することにより、前記酸化セ
リウムを担持させた前記ハニカム担体に、Al2 O3
 皮膜を形成する担持助剤と共に付着させたものである
[Means for Solving the Problems] In order to achieve the above object, the exhaust gas purification catalyst of the present invention is provided by applying cerium oxide to a honeycomb carrier of heat-resistant ceramics mainly composed of cordierite, and further applying ABO3 basic fine powder of perovskite composite oxide having a structure, fine zirconia powder, iron oxide, and one or more elements among noble metal elements such as platinum, palladium, and rhodium, and alumina sol,
Al2O3 is added to the honeycomb carrier on which the cerium oxide is supported by firing with aluminum nitrate.
It is attached together with a supporting agent that forms a film.

【0006】[0006]

【作用】上記構成によって本発明の排ガス浄化触媒は、
ハニカム担体の露出面を酸化セリウムで完全に被うこと
により、アルミニウムとペロブスカイト複合酸化物(A
BO3)のBサイト成分である遷移金属元素との間のス
ピネル化合物の生成を押えることができ、またペロブス
カイト複合酸化物、酸化セリウムの他に酸化ジルコニウ
ム及び一種類以上の貴金属元素を主体とする組成物とす
ることにより、200℃以上の高温で還元性雰囲気にお
いても貴金属の粒成長や、貴金属のペロブスカイト複合
酸化物中への拡散を抑制することとなる。
[Operation] With the above configuration, the exhaust gas purification catalyst of the present invention has
By completely covering the exposed surface of the honeycomb carrier with cerium oxide, aluminum and perovskite composite oxide (A
It is possible to suppress the formation of a spinel compound with the transition metal element which is the B site component of BO3), and the composition mainly contains perovskite composite oxide, zirconium oxide and one or more noble metal elements in addition to cerium oxide. By making it a perovskite composite oxide, grain growth of the noble metal and diffusion of the noble metal into the perovskite composite oxide can be suppressed even in a reducing atmosphere at a high temperature of 200° C. or higher.

【0007】[0007]

【実施例】以下本発明の一実施例の排ガス浄化触媒につ
いて図面を基にして説明する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS An exhaust gas purification catalyst according to an embodiment of the present invention will be described below with reference to the drawings.

【0008】市販のコーディエライト(2MgO・5S
iO2 ・2Al2 O3)質ハニカム担体(日本ガイ
シ製)を用いて触媒を調整した。用いたハニカム担体は
横断面が1インチ平方当り約400個のガス流通セルを
有する外径76mmφ、長さ75mmLの円柱状のもの
で、約340mlの体積を有した。
[0008] Commercially available cordierite (2MgO・5S
A catalyst was prepared using an iO2 .2Al2 O3) honeycomb carrier (manufactured by NGK Insulators). The honeycomb carrier used had a cylindrical cross section with an outer diameter of 76 mm and a length of 75 mm, having a cross section of about 400 gas flow cells per square inch, and had a volume of about 340 ml.

【0009】硝酸セリウム〔Ce(NO3)3 ・6H
2 O〕を純水に溶解して、比重1.33の水溶液とし
、この硝酸セリウム水溶液に前記ハニカム担体を浸漬し
た後取り出し、前記ハニカム担体内の過剰硝酸セリウム
水溶液を圧縮空気でブローして除去する。次に100℃
乾燥空気で30分乾燥後800℃空気中で1時間焼成さ
せ、酸化セリウム(CoO2)を担持させたものを得た
。次にアルカリ沈澱法(作製法の詳細は省略)で作製し
た、ABO3(AはLa、Ce、Srなどの希土類元素
またはアルカリ土類元素の中少なくとも一種類の元素、
BはCo、Niなど遷移金属元素の中少なくとも一種類
の元素)の基本構造を有するペロブスカイト複合酸化物
の中、La0.9 Ce0.1 CoO3 の構造を有
するペロブスカイト複合酸化物の微粒子(表面積19.
8m2/g、一次粒子径1μ以下)100g、酸化ジル
コニウム(ZrO2)の粉末20gアルミナゾル(酢酸
酸性、固型分1/10)50g、硝酸パラジウム〔Pd
(NO3)2 〕0.9g、硝酸第二鉄〔Fe(NO3
)3 ・9H2 O〕4.3g及び水150gを混合攪
拌してスラリーを調整し、この中に上記コーディエライ
ト質ハニカム担体を浸漬し、引き上げた後、セル内の過
剰スラリーを圧縮空気でブローして全ての目詰りを除去
した。次に200℃で1時間乾燥空気で乾燥後650℃
で焼成した。
Cerium nitrate [Ce(NO3)3 .6H
2 O] in pure water to make an aqueous solution with a specific gravity of 1.33, the honeycomb carrier was immersed in this aqueous cerium nitrate solution and then taken out, and the excess cerium nitrate aqueous solution in the honeycomb carrier was removed by blowing with compressed air. do. Then 100℃
After drying in dry air for 30 minutes, it was calcined in air at 800°C for 1 hour to obtain a product on which cerium oxide (CoO2) was supported. Next, ABO3 (A is at least one element among rare earth elements such as La, Ce, and Sr or alkaline earth elements,
B is at least one element among transition metal elements such as Co and Ni) Among perovskite composite oxides having a basic structure of La0.9 Ce0.1 CoO3, fine particles of perovskite composite oxide with a structure of La0.9 Ce0.1 CoO3 (surface area 19.
8m2/g, primary particle size 1μ or less) 100g, 20g of zirconium oxide (ZrO2) powder, 50g of alumina sol (acidic acid, solid content 1/10), palladium nitrate [Pd
(NO3)2] 0.9g, ferric nitrate [Fe(NO3)
)3 ・9H2 O] 4.3 g and 150 g of water were mixed and stirred to prepare a slurry, the cordierite honeycomb carrier was immersed in the slurry, and after being pulled up, the excess slurry in the cells was blown with compressed air. to remove all clogging. Next, dry at 200℃ for 1 hour with dry air and then 650℃
It was fired in

【0010】焼成後の触媒体の構成は前コートの酸化セ
リウムも含めた触媒組成物約24重量%、担体約76重
量%であり、触媒組成物中のペロブスカイト型複合酸化
物48.5重量%、酸化セリウムは38.8重量%、酸
化ジルコニウムは9.7重量%、酸化アルミニウム2.
4重量%、パラジウムは0.27重量%、酸化鉄は0.
28重量%であった。
[0010] The composition of the catalyst body after firing is about 24% by weight of the catalyst composition including the cerium oxide of the pre-coat, about 76% by weight of the carrier, and 48.5% by weight of the perovskite type composite oxide in the catalyst composition. , cerium oxide 38.8% by weight, zirconium oxide 9.7% by weight, aluminum oxide 2.
4% by weight, palladium 0.27% by weight, iron oxide 0.
It was 28% by weight.

【0011】(比較例1)比較例として市販のコーディ
エライト(実施例と同一物)を用い酸化セリウム(Ce
O2)を担持させた。(担持法は実施例と同じ)次にア
ルカリ沈澱法(作製法の詳細は省略)で作製したLa0
.9 Ce0.1 CoO3 の構造を有するペロブス
カイト複合酸化物微粒子(表面積19.8m2/g、一
次粒子1μ以下)100gと酢酸酸性アルミナゾル50
g(日産化学製)及び水をそれぞれの重量比1:1:1
のものをボールミル混練機を用いよく混練し、さらに水
を加え、比重121になるように調整し、ペロブスカイ
ト酸化物スラリーを作製した。このスラリーに前記Ce
O2 を担持させた担体を浸漬し、引き上げた後、セル
内の過剰スラリーを圧縮空気でブローして全ての目詰り
を除去した。次に200℃で1時間乾燥空気で乾燥後8
00℃で焼成した。 次に上記担体1l当り400mgのパラジウム(Pd)
を担持する。含浸させることにより担体1l当り400
mgになるように硝酸パラジウム〔Pd(NO3)2 
〕水溶液を調整し、その中に前記担体を浸漬し、担体内
の過剰水溶液を圧縮空気でブローして全てのセルの目詰
りを除去した。次に100℃乾燥空気で1時間乾燥後6
00℃空気中で30分間焼成させ、所定量のパラジウム
を担持させた。
(Comparative Example 1) As a comparative example, commercially available cordierite (same as the example) was used, and cerium oxide (Ce
O2) was supported. (The supporting method is the same as in the example.) Next, La0 was prepared by the alkaline precipitation method (details of the preparation method are omitted).
.. 9 100 g of perovskite composite oxide fine particles having a structure of Ce0.1 CoO3 (surface area 19.8 m2/g, primary particles 1 μ or less) and 50 g of acetic acid acidic alumina sol
g (manufactured by Nissan Chemical) and water at a weight ratio of 1:1:1.
The mixture was thoroughly kneaded using a ball mill kneader, water was added, and the specific gravity was adjusted to 121 to prepare a perovskite oxide slurry. In this slurry, the Ce
After the carrier loaded with O2 was immersed and pulled up, the excess slurry in the cell was blown out with compressed air to remove any clogging. Next, after drying with dry air at 200℃ for 1 hour,
It was fired at 00°C. Next, 400 mg of palladium (Pd) per liter of the above carrier.
to carry. 400 per liter of carrier by impregnating
palladium nitrate [Pd(NO3)2
] An aqueous solution was prepared, the carrier was immersed therein, and the excess aqueous solution in the carrier was blown out with compressed air to remove clogging from all cells. Next, after drying for 1 hour in dry air at 100℃,
It was fired in air at 00°C for 30 minutes to support a predetermined amount of palladium.

【0012】(比較例2)別の比較例として市販のコー
ディエライト(実施例と同一物)を用い酸化セリウム(
CeO2)を担持させた。(担持法は実施例と同じ)、
次にアルカリ沈澱法(作製法の詳細は省略)で作製した
La0.9 Ce0.1 CoO3 の構造を有するペ
ロブスカイト複合酸化物微粒子(表面積19.8m2/
g、一次粒子1μ以下)100gと、酢酸酸性アルミナ
ゾル50g、硝酸パラジウム〔Pd(NO3)2 〕1
.0g及び水140gを混合攪拌してスラリーを調整し
、この中に上記コーディエライトハニカム担体を浸漬し
、引き上げた後セル内の過剰のスラリーを圧縮空気でブ
ローして全ての目詰りを除去した。次に200℃で1時
間乾燥空気で乾燥後650℃で焼成した。
(Comparative Example 2) As another comparative example, commercially available cordierite (same as in Example) was used, and cerium oxide (
CeO2) was supported. (The loading method is the same as in the example),
Next, perovskite composite oxide fine particles with a structure of La0.9 Ce0.1 CoO3 (surface area 19.8 m2/
g, primary particles 1μ or less), 50 g of acetic acid acidic alumina sol, palladium nitrate [Pd(NO3)2] 1
.. A slurry was prepared by mixing and stirring 0 g and 140 g of water, into which the cordierite honeycomb carrier was immersed, and after being pulled up, the excess slurry in the cells was blown with compressed air to remove all clogging. . Next, it was dried at 200°C for 1 hour with dry air and then fired at 650°C.

【0013】上記で作製した3種類の触媒体について触
媒性能の初期特性と耐久性を比較した。
[0013] The three types of catalyst bodies produced above were compared in terms of initial characteristics of catalyst performance and durability.

【0014】試験条件は次の通りであり、試験結果を(
表1)に示す。
[0014] The test conditions were as follows, and the test results were expressed as (
Table 1) shows the results.

【0015】[0015]

【表1】[Table 1]

【0016】触媒性能試験条件として、ガス組成(容量
基準)として、NO1%、CO1%、ヘリウム98%で
構成する反応ガスを用いた。また、空間速度を1250
0/Hrとした。さらに、測定方法としては、固定床流
通式により反応を行ないガスクロマトグラフィーにより
NOのN2 への転換率を求めた。反応温度は300℃
である。
As the catalyst performance test conditions, a reaction gas consisting of 1% NO, 1% CO, and 98% helium was used as the gas composition (based on volume). Also, the space velocity is 1250
It was set as 0/Hr. Furthermore, as a measurement method, the reaction was carried out using a fixed bed flow system, and the conversion rate of NO to N2 was determined using gas chromatography. Reaction temperature is 300℃
It is.

【0017】(表1)より、触媒性能の耐久性に対して
は、ジルコニアと酸化鉄の共存が必須であることが明き
らかである。
From Table 1, it is clear that the coexistence of zirconia and iron oxide is essential for the durability of catalyst performance.

【0018】次に上記3種類の触媒体について、触媒性
能の経時変化を測定した。図1において本実施例の触媒
体は優れた耐久性を示した。
Next, changes in catalyst performance over time were measured for the three types of catalyst bodies mentioned above. In FIG. 1, the catalyst body of this example showed excellent durability.

【0019】この時の試験条件は次の通りである。触媒
を900℃で電気炉で空気中処理し活性の変化を調べた
The test conditions at this time were as follows. The catalyst was treated in air at 900°C in an electric furnace and changes in activity were examined.

【0020】ガス組成(容量基準)として、NO1%、
CO1%、ヘリウム98%で構成する反応ガスを用いた
。また空間速度を12500/Hrとした。さらに、測
定方法としては、固定床流通式により反応を行ない、ガ
スクロストグラフィーによりNOのN2 への転換率を
求めた。反応温度は300℃である。
[0020] Gas composition (volume basis): NO1%,
A reaction gas consisting of 1% CO and 98% helium was used. Moreover, the space velocity was set to 12500/Hr. Furthermore, as a measuring method, the reaction was carried out using a fixed bed flow system, and the conversion rate of NO to N2 was determined by gas clostography. The reaction temperature is 300°C.

【0021】なお実施例では貴金属の例としてパラジウ
ムを用いた場合について説明したが、パラジウムの他に
一部又は全部を白金、ロジウムを用いても同様の効果が
得られた。
[0021] In the examples, the case where palladium was used as an example of the noble metal was explained, but similar effects could be obtained by using platinum or rhodium in part or in whole in addition to palladium.

【0022】[0022]

【発明の効果】以上の実施例の説明で明らかなように本
発明の排ガス浄化触媒によれば、アルミナを含有してい
る担体の露出面を酸化セリウムで完全に被うことにより
、アルミニウムとペロブスカイト複合酸化物(ABO3
)のBサイト成分である遷移金属との間のスピネル化合
物の生成を押えることができ、またペロブスカイト複合
酸化物、酸化セリウムの他に酸化ジルコニウム、及び一
種類以上の貴金属元素を主体とする組成物とすることに
より、200℃以上の高温で還元雰囲気中においても貴
金属の粒成長や、貴金属のペロブスカイト複合酸化物中
への拡散を抑制する耐久性の優れたものとなる。
Effects of the Invention As is clear from the above description of the embodiments, according to the exhaust gas purification catalyst of the present invention, by completely covering the exposed surface of the carrier containing alumina with cerium oxide, aluminum and perovskite Complex oxide (ABO3
) can suppress the formation of a spinel compound with the transition metal that is the B site component, and is a composition mainly containing perovskite composite oxide, zirconium oxide in addition to cerium oxide, and one or more noble metal elements. By doing so, it has excellent durability that suppresses the grain growth of the noble metal and the diffusion of the noble metal into the perovskite composite oxide even in a reducing atmosphere at a high temperature of 200° C. or higher.

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

【図1】本発明の一実施例と比較例の触媒性能の耐久性
を示すグラフ
[Figure 1] Graph showing durability of catalyst performance of an example of the present invention and a comparative example

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】コーデイエライト質を主体とする耐熱性セ
ラミックスから構成されるハニカム担体の内部の多数の
細孔に硝酸セリウム溶液を含浸させ、焼成することによ
り前記ハニカム担体に酸化セリウムを担持させ、さらに
その上からABO3(AはLa、Ce、Srなど希土類
またはアルカリ土類元素の中少なくとも一種類の元素、
BはCo、Niなど遷移金属元素の中少なくとも一種類
の元素)の基本構造を有するペロブスカイト複合酸化物
の微粉末、ジルコニア微粉末、酸化鉄、及び白金、パラ
ジウム、ロジウムなどの貴金属元素の中の一種類以上の
元素と、アルミナゾル、硝酸アルミニウムとを焼成する
ことにより、前記酸化セリウムを担持させた前記ハニカ
ム担体に、Al2 O3 皮膜を形成する担持助剤と共
に付勢させた排ガス浄化触媒。
[Claim 1] Cerium oxide is supported on the honeycomb carrier by impregnating a cerium nitrate solution into a large number of pores inside a honeycomb carrier made of heat-resistant ceramics mainly composed of cordierite, and firing the honeycomb carrier. , and then ABO3 (A is at least one element among rare earth or alkaline earth elements such as La, Ce, and Sr,
B is fine powder of perovskite composite oxide having a basic structure of at least one element among transition metal elements such as Co and Ni, fine zirconia powder, iron oxide, and noble metal elements such as platinum, palladium, and rhodium. An exhaust gas purification catalyst in which the honeycomb carrier supporting the cerium oxide is energized together with a supporting agent that forms an Al2 O3 film by firing one or more types of elements, alumina sol, and aluminum nitrate.
JP03058640A 1991-03-22 1991-03-22 Exhaust gas purification catalyst Expired - Fee Related JP3099392B2 (en)

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CN111801159A (en) * 2018-05-11 2020-10-20 株式会社村田制作所 Honeycomb catalyst for organic matter decomposition and organic matter decomposition device

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CN101947456B (en) * 2010-08-19 2013-02-13 华南理工大学 Integral automobile exhaust purification catalyst and preparation method thereof

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111801159A (en) * 2018-05-11 2020-10-20 株式会社村田制作所 Honeycomb catalyst for organic matter decomposition and organic matter decomposition device
CN111801159B (en) * 2018-05-11 2023-07-07 株式会社村田制作所 Honeycomb structured catalyst for decomposing organic matter and organic matter decomposing apparatus

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