JP2003290658A - Catalyst for cleaning exhaust gas and manufacture method therefor - Google Patents

Catalyst for cleaning exhaust gas and manufacture method therefor

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Publication number
JP2003290658A
JP2003290658A JP2002100157A JP2002100157A JP2003290658A JP 2003290658 A JP2003290658 A JP 2003290658A JP 2002100157 A JP2002100157 A JP 2002100157A JP 2002100157 A JP2002100157 A JP 2002100157A JP 2003290658 A JP2003290658 A JP 2003290658A
Authority
JP
Japan
Prior art keywords
exhaust gas
catalyst
metal
supported
noble metal
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
JP2002100157A
Other languages
Japanese (ja)
Inventor
Yusuke Ito
祐介 伊藤
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
Original Assignee
Toyota Motor Corp
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 Motor Corp filed Critical Toyota Motor Corp
Priority to JP2002100157A priority Critical patent/JP2003290658A/en
Publication of JP2003290658A publication Critical patent/JP2003290658A/en
Pending legal-status Critical Current

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Abstract

<P>PROBLEM TO BE SOLVED: To provide a catalyst for cleaning an exhaust gas in which a amount of a noble metal carried is reduced and sintering is inhibited. <P>SOLUTION: The catalyst for cleaning the exhaust gas is characterized in that an oxide carrier is carried with at least one metal particle of W or Mo and the metal particle is carried with the noble metal. The metal particle preferably has a diameter of 1-15 nm and a mass ratio of the noble metal/metal particle is 1-10. The catalyst for cleaning the exhaust gas can be manufactured by reducing/precipitating the noble metal on the at least one metal particle of W or Mo. <P>COPYRIGHT: (C)2004,JPO

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、貴金属の担持量が
削減され、かつシンタリングが抑制された排気ガス浄化
用触媒に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying catalyst in which the amount of precious metal carried is reduced and sintering is suppressed.

【0002】[0002]

【従来の技術】自動車用エンジン等の内燃機関から排出
される排気ガスには、一酸化炭素(CO)、炭化水素(H
C)、窒素酸化物(NOX)等が含まれ、これらの有害物質
は、一般に、白金(Pt)、パラジウム(Pd)、ロジウム
(Rh)等の貴金属を触媒成分とする排気ガス浄化用触媒
によって浄化される。
2. Description of the Related Art Exhaust gas emitted from an internal combustion engine such as an automobile engine contains carbon monoxide (CO), hydrocarbon (H
C), nitrogen oxides (NO x ), etc., and these harmful substances are generally platinum (Pt), palladium (Pd), rhodium.
It is purified by an exhaust gas purification catalyst containing a precious metal such as (Rh) as a catalyst component.

【0003】[0003]

【発明が解決しようとする課題】しかるに、環境保護の
面から、これらの排気ガス浄化用触媒は、より一層の浄
化性能の向上が要請されており、従来は、主として、触
媒成分としての貴金属の担持量を増加させることでこの
対応がなされてきた。しかし、貴金属は高価であり、採
掘量にも限りがある。
However, from the viewpoint of environmental protection, these exhaust gas purifying catalysts are required to have further improved purifying performance, and conventionally, mainly, noble metal as a catalyst component is used. This has been done by increasing the loading amount. However, precious metals are expensive and the amount of mining is limited.

【0004】一方、排気ガス浄化用触媒は、一般に、常
温と約1000℃の間で温度が繰り返して変動し、かつ
比較的HCとCOの濃度が高くてO2濃度が低い還元性
雰囲気と、比較的HCとCOの濃度が低くてO2濃度が
高い酸化性雰囲気が繰り返される条件下で使用される。
On the other hand, the exhaust gas purifying catalyst generally has a reducing atmosphere in which the temperature repeatedly changes between room temperature and about 1000 ° C., and the concentration of HC and CO is relatively high and the O 2 concentration is low. It is used under conditions where an oxidizing atmosphere with a relatively low concentration of HC and CO and a high concentration of O 2 is repeated.

【0005】しかし、上記の貴金属の触媒成分には、こ
うした雰囲気に長期間曝されると触媒成分が担体上を移
動して肥大化した粒子を形成する、いわゆるシンタリン
グを生じる性質があり、このため排気ガス浄化性能が経
時的に低下するという問題がある。
However, the above noble metal catalyst component has a property of causing so-called sintering, in which the catalyst component moves on the carrier to form enlarged particles when exposed to such an atmosphere for a long time. Therefore, there is a problem that the exhaust gas purification performance deteriorates with time.

【0006】ところで、本出願人は、特開2001−4
6870号公報において、PtとWを含む複合酸化物を
触媒成分とする排気ガス浄化用触媒を提案し、また、特
開平11−156193号公報において、種々の合金触
媒が担持された排気ガス浄化用触媒を提案している。
[0006] By the way, the applicant of the present invention has disclosed in Japanese Patent Laid-Open No. 2001-4.
No. 6870 proposes an exhaust gas purifying catalyst containing a complex oxide containing Pt and W as a catalyst component, and in Japanese Patent Laid-Open No. 11-156193, there is proposed an exhaust gas purifying catalyst carrying various alloy catalysts. Proposing a catalyst.

【0007】本発明は、かかる公知技術とは全く異なる
構成の排気ガス浄化用触媒により、貴金属の担持量が削
減され、かつシンタリングが抑制された排気ガス浄化用
触媒を提供することを目的とする。
It is an object of the present invention to provide an exhaust gas purifying catalyst in which the amount of precious metal carried is reduced and sintering is suppressed by the exhaust gas purifying catalyst having a structure completely different from that of the known art. To do.

【0008】[0008]

【課題を解決するための手段】上記の目的は、W又はM
oの少なくとも一方の金属粒子が酸化物担体に担持さ
れ、前記金属粒子の上に貴金属が担持されたことを特徴
とする排気ガス浄化用触媒によって達成される。即ち、
本発明の排気ガス浄化用触媒は、コア状のW又はMoの
金属粒子の周りに貴金属がシェル状に担持されてなる触
媒である。かかる構成の排気ガス浄化用触媒によって上
記の目的が達成される理由は、次のように考えられる。
The above-mentioned objects are W or M.
This is achieved by an exhaust gas purifying catalyst characterized in that at least one metal particle of o is supported on an oxide carrier, and a noble metal is supported on the metal particle. That is,
The exhaust gas purifying catalyst of the present invention is a catalyst in which a noble metal is supported in a shell shape around a core of W or Mo metal particles. The reason why the above object is achieved by the exhaust gas purifying catalyst having such a structure is considered as follows.

【0009】排気ガス中の有害物質は、酸化物担体に担
持された貴金属の触媒成分に接触することにより反応浄
化されるため、実質的には、貴金属の表面のみが有効な
触媒成分となる。しかしながら、貴金属の全てを原子レ
ベルの薄さで酸化物担体上に担持するのは困難であり、
また、貴金属は、上記のようにシンタリングによって肥
大化した粒子に変化する性質を有する。これらの場合、
貴金属粒子のコア部分は、実質的に、触媒成分として寄
与することができない。
The harmful substances in the exhaust gas are purified by reaction by contacting the noble metal catalyst component supported on the oxide carrier, so that substantially only the noble metal surface becomes an effective catalyst component. However, it is difficult to support all of the noble metals on the oxide support with atomic level thinness,
Further, the noble metal has a property of changing into particles enlarged by sintering as described above. In these cases,
The core portion of the noble metal particles cannot substantially contribute as a catalyst component.

【0010】ここで、酸化物担体とW又はMoは、それ
らの界面で酸素を介することで、結合強度が高くなり、
上記の排気ガス雰囲気下でも、W又はMoの金属粒子の
形態を実質的に変化させることはない。さらに、貴金属
とW又はMoもまた、これらの界面での結合強度が高
く、W又はMoの金属粒子の上に担持された貴金属は、
上記の排気ガス雰囲気下での移動が抑制され、したがっ
てシンタリングが実質的に生じない。
Here, the oxide carrier and W or Mo have a high bond strength due to the intervening oxygen at their interface,
Even under the above exhaust gas atmosphere, the morphology of the metal particles of W or Mo is not substantially changed. Furthermore, the noble metal and W or Mo also have a high bond strength at their interface, and the noble metal supported on the W or Mo metal particles is
The movement under the exhaust gas atmosphere is suppressed, and therefore sintering is substantially not caused.

【0011】このため、W又はMoの金属粒子をコアと
し、その上に貴金属を微粒子又は極めて薄い膜状に担持
すれば、そのコアに相当する体積の貴金属の量が実質的
に削減され、かつシンタリングを抑えることができる。
図1は、かかる本発明の排気ガス浄化用触媒のモデル図
である。なお、本発明はこのモデル図に限定されるもの
ではない。
Therefore, by using W or Mo metal particles as a core and supporting the precious metal in the form of fine particles or an extremely thin film thereon, the amount of the precious metal in a volume corresponding to the core is substantially reduced, and Sintering can be suppressed.
FIG. 1 is a model diagram of the exhaust gas purifying catalyst of the present invention. The present invention is not limited to this model diagram.

【0012】[0012]

【発明の実施の形態】本発明の排気ガス浄化用触媒は、
W又はMoの少なくとも一方の金属粒子が酸化物担体に
担持され、前記金属粒子の上に貴金属が担持されて構成
される。酸化物担体としては、アルミナ、シリカ、ジル
コニアのような酸化物のほか、シリカ-アルミナ、セリ
ア-ジルコニア、アルミナ-セリア-ジルコニア、セリア-
ジルコニア-イットリア、ジルコニア-カルシアのような
複合酸化物が挙げられ、平均粒子径が1μm以下の微粒
子からなるものが好適に使用可能である。
BEST MODE FOR CARRYING OUT THE INVENTION The exhaust gas purifying catalyst of the present invention comprises:
At least one metal particle of W or Mo is supported on an oxide carrier, and a noble metal is supported on the metal particle. As the oxide carrier, in addition to oxides such as alumina, silica and zirconia, silica-alumina, ceria-zirconia, alumina-ceria-zirconia, ceria-
Examples thereof include complex oxides such as zirconia-yttria and zirconia-calcia, and those composed of fine particles having an average particle diameter of 1 μm or less can be preferably used.

【0013】このような酸化物担体にW及び/又はMo
を担持するのは、タングステン酸アンモニウムパラ五水
和物5(NH4)2・12WO3・5H2O、メタタングステ
ン酸アンモニウム(NH4)6[H21240]、七モリブ
デン酸六アンモニウム四水和物(NH4)6Mo724・4
2O、メタモリブデン酸アンモニウム(NH4)4[Mo 8
26]のような水等の溶媒に溶解する化合物の溶液、又
はこれらの化合物の混合溶液を酸化物担体の粉末に含浸
し、次いで、乾燥・焼成することによって行うことがで
きる。
W and / or Mo may be added to such an oxide support.
Carrying ammonium tungstate para pentahydrate
Japanese product 5 (NHFour)2・ 12 WO3・ 5H2O, metatungsten
Ammonium acid (NHFour)6[H2W12O40], Seven morib
Hexammonium decanoate tetrahydrate (NHFour)6Mo7Otwenty four・ 4
H2O, ammonium metamolybdate (NHFour)Four[Mo 8
O26] A solution of a compound soluble in a solvent such as water, or
Impregnates oxide support powder with a mixed solution of these compounds
And then drying and firing.
Wear.

【0014】あるいは、三酸化タングステンWO3、三
酸化モリブデンMoO3のような微粉末又はこれらの混
合微粉末を酸化物担体の粉末と混合し、次いで、乾燥・
焼成することによって担持することもできる。
Alternatively, a fine powder such as tungsten trioxide WO 3 , molybdenum trioxide MoO 3 or a mixed fine powder thereof is mixed with a powder of an oxide carrier and then dried.
It can also be supported by firing.

【0015】次いで、このW及び/又はMoが担持され
た酸化物担体上に貴金属が担持される。この担持の仕方
は、ジニトロジアンミン白金錯体Pt(NH3)2(N
2)2、塩化白金酸H2PtCl6・6H2O、白金アセチ
ルアセトナートPt(acac)2、硝酸パラジウムPd
(NO3)2、塩化パラジウムPdCl2、硝酸ロジウムR
h(NO3)3、塩化ロジウムRhCl3・4H2O等の溶解
性貴金属化合物を用い、これらの化合物の溶液を好適な
pHに調整した上で酸化物担体の粉末に含浸し、次い
で、乾燥・焼成することによって行うことができる。
Next, a noble metal is supported on the W and / or Mo-supported oxide carrier. This supporting method is based on the dinitrodiammine platinum complex Pt (NH 3 ) 2 (N
O 2 ) 2 , chloroplatinic acid H 2 PtCl 6 .6H 2 O, platinum acetylacetonate Pt (acac) 2 , palladium nitrate Pd
(NO 3 ) 2 , palladium chloride PdCl 2 , rhodium nitrate R
Using soluble noble metal compounds such as h (NO 3 ) 3 and rhodium chloride RhCl 3 .4H 2 O, the solution of these compounds was adjusted to a suitable pH, impregnated into the oxide carrier powder, and then dried. -Can be performed by firing.

【0016】好ましくは、貴金属の担持は、還元析出に
よって行う。より詳しくは、上記のW及び/又はMoが
担持された酸化物担体を水に分散させてスラリーにし、
これに上記の貴金属化合物を溶解させる。次いで、この
スラリーに、ヒドラジンN24、チオ硫酸ナトリウムN
223、チオ硫酸カリウムK223、チオ硫酸アン
モニウム(NH4)223、亜硫酸ナトリウムNa2
3、水素化ホウ素ナトリウムNaBH4等のホウ水素化
物、次亜リン酸塩、クエン酸塩、ギ酸CH22、シュウ
酸CH24等の還元剤と、L-アスコルビン酸ナトリウム
676Na、エチレンジアミン四酢酸塩等の緩衝剤
を添加して貴金属化合物を還元し、Pt等の貴金属を微
細な形態で析出させる。
[0016] Preferably, the noble metal is supported by reduction precipitation. More specifically, the above oxide carrier supporting W and / or Mo is dispersed in water to form a slurry,
The above noble metal compound is dissolved in this. Then, add hydrazine N 2 H 4 and sodium thiosulfate N to the slurry.
a 2 S 2 O 3 , potassium thiosulfate K 2 S 2 O 3 , ammonium thiosulfate (NH 4 ) 2 S 2 O 3 , sodium sulfite Na 2 S
O 3 , borohydrides such as sodium borohydride NaBH 4 , etc., reducing agents such as hypophosphite, citrate, formic acid CH 2 O 2 and oxalic acid CH 2 O 4 , and sodium L-ascorbate C 6 A noble metal compound is reduced by adding a buffering agent such as H 7 O 6 Na or ethylenediaminetetraacetic acid salt to precipitate a noble metal such as Pt in a fine form.

【0017】こうした還元析出によれば、貴金属を原子
レベルの単位の微粒子又は極めて薄い膜状で、実質的に
全てW及び/又はMoの上に析出させることが比較的容
易である。次いで、好ましくは、大気中で300〜70
0℃の温度に数時間加熱して焼成することにより、貴金
属を強固に担持することができる。
According to such reduction deposition, it is relatively easy to deposit the noble metal in the form of fine particles of an atomic level unit or an extremely thin film on substantially all W and / or Mo. Then, preferably 300 to 70 in the atmosphere.
By heating at a temperature of 0 ° C. for several hours and firing, the precious metal can be firmly supported.

【0018】このようにして得られる本発明の触媒担体
において、W又はMoの金属粒子は好ましくは1〜15
nm、より好ましくは1〜10nmの直径を有する。こ
の直径は、上記のW又はMo化合物の種類と濃度、焼成
条件等によって制御することができる。
In the catalyst carrier of the present invention thus obtained, the metal particles of W or Mo are preferably 1 to 15
nm, more preferably 1-10 nm. This diameter can be controlled by the type and concentration of the above W or Mo compound, firing conditions, and the like.

【0019】なお、貴金属/W又はMoの質量比は、好
ましくは1〜10、より好ましくは2〜5であり、酸化
物担体に担持された「W又はMoの金属粒子」とは、酸
化タングステンと酸化モリブデンの金属酸化物、及びW
又はMoの金属の双方を含む意味である。
The mass ratio of noble metal / W or Mo is preferably 1 to 10, more preferably 2 to 5, and the "metal particles of W or Mo" carried on the oxide carrier means tungsten oxide. And molybdenum oxide metal oxides, and W
Alternatively, it is meant to include both Mo metals.

【0020】このようにして調製された本発明の排気ガ
ス浄化用触媒は、モノリス基材にコートされて、あるい
はペレット状にされて、内燃機関の排気ガス浄化に使用
されることができる。以下、実施例によって本発明をよ
り具体的に説明する。
The exhaust gas purifying catalyst of the present invention thus prepared can be used for purifying exhaust gas of an internal combustion engine by coating it on a monolith substrate or pelletizing it. Hereinafter, the present invention will be described more specifically with reference to Examples.

【0021】[0021]

【実施例】実施例1 以下のようにして、酸化物担体のCeO2-ZrO2粉末
(Ce/Zrのモル比=1/1、比表面積70m2/g)
にW粒子が担持され、このW粒子の上にPtが担持され
た4通りの本発明の排気ガス浄化用触媒を調製した。C
eO2-ZrO2粉末にタングステン酸アンモニウムパラ
五水和物の水溶液を含浸させた後、大気雰囲気中で50
0℃×2時間の焼成に供して、CeO2-ZrO2粉末に
W粒子を担持した。
EXAMPLES Example 1 CeO 2 --ZrO 2 powder as an oxide carrier was prepared as follows.
(Molar ratio of Ce / Zr = 1/1, specific surface area 70 m 2 / g)
Four types of exhaust gas purifying catalysts of the present invention were prepared in which W particles were supported on Pt and Pt was supported on the W particles. C
eO 2 -ZrO 2 after the powder is impregnated with an aqueous solution of ammonium tungstate para pentahydrate, 50 in the atmosphere
It was subjected to calcination at 0 ° C. for 2 hours, and W particles were supported on the CeO 2 —ZrO 2 powder.

【0022】このW/CeO2-ZrO2粉末を、表1に
示す量で、60℃のイオン交換水の2000gに分散さ
せ、得られたスラリーに、水素化ホウ素ナトリウムを
0.20質量%の濃度、アスコルビン酸ナトリウムを2.
00質量%の濃度、及び塩化白金酸を表1に示す濃度と
なる量で順次に添加し、穏やかな攪拌下に24時間置く
ことでH2PtCl6からPtを還元析出させた。
This W / CeO 2 -ZrO 2 powder was dispersed in 2000 g of ion-exchanged water at 60 ° C. in an amount shown in Table 1, and 0.20% by mass of sodium borohydride was added to the obtained slurry. Concentration, sodium ascorbate 2.
A concentration of 00% by mass and chloroplatinic acid were sequentially added in the amounts shown in Table 1, and the mixture was placed under gentle stirring for 24 hours to reduce and precipitate Pt from H 2 PtCl 6 .

【0023】この還元析出の後、スラリーを濾過・洗浄
し、大気中で120℃×2時間の乾燥を行い、さらに大
気中で500℃×2時間の熱処理を行った。この方法に
より表1に示す組成の4通りの排気ガス浄化用触媒を得
た。
After this reduction precipitation, the slurry was filtered and washed, dried at 120 ° C. for 2 hours in the atmosphere, and further heat-treated at 500 ° C. for 2 hours in the atmosphere. By this method, four kinds of exhaust gas purifying catalysts having the compositions shown in Table 1 were obtained.

【0024】[0024]

【表1】 [Table 1]

【0025】実施例2 以下のようにして、酸化物担体のCeO2-ZrO2粉末
にMo粒子が担持され、このMo粒子の上にPtが担持
された4通りの本発明の排気ガス浄化用触媒を調製し
た。CeO2-ZrO2粉末に七モリブデン酸六アンモニ
ウム四水和物の水溶液を含浸させた後、大気雰囲気中で
500℃×2時間の焼成に供して、CeO2-ZrO 2
末にMo粒子を担持した。
Example 2 The CeO of the oxide support is prepared as follows.2-ZrO2Powder
Mo particles are supported on, and Pt is supported on the Mo particles.
Prepared four kinds of exhaust gas purifying catalysts of the present invention
It was CeO2-ZrO26 Ammonium heptamolybdate in powder
After impregnating with an aqueous solution of um tetrahydrate, in an air atmosphere
CeO provided by firing at 500 ° C x 2 hours2-ZrO 2powder
Finally, Mo particles were supported.

【0026】このMo/CeO2-ZrO2粉末を、表2
に示す量で、60℃のイオン交換水の2000gに分散
させ、得られたスラリーに、水素化ホウ素ナトリウムを
0.20質量%の濃度、アスコルビン酸ナトリウムを2.
00質量%の濃度、及び塩化白金酸を表2に示す濃度と
なる量で順次に添加し、穏やかな攪拌下に24時間置く
ことでH2PtCl6からPtを還元析出させた。
This Mo / CeO 2 -ZrO 2 powder is shown in Table 2.
In the amount shown in (2), 2000 g of ion-exchanged water at 60 ° C. was dispersed, and the obtained slurry had a sodium borohydride concentration of 0.20% by mass and sodium ascorbate of 2.
A concentration of 00% by mass and chloroplatinic acid were sequentially added in the amounts shown in Table 2, and the mixture was placed under gentle stirring for 24 hours to reduce and precipitate Pt from H 2 PtCl 6 .

【0027】この還元析出の後、スラリーを濾過・洗浄
し、大気中で120℃×2時間の乾燥を行い、さらに大
気中で500℃×2時間の熱処理を行った。この方法に
より表2に示す組成の4通りの排気ガス浄化用触媒を得
た。
After this reduction precipitation, the slurry was filtered and washed, dried at 120 ° C. for 2 hours in the atmosphere, and further heat-treated at 500 ° C. for 2 hours in the atmosphere. By this method, four kinds of exhaust gas purifying catalysts having the compositions shown in Table 2 were obtained.

【0028】[0028]

【表2】 [Table 2]

【0029】比較例1 CeO2-ZrO2粉末にジニトロジアンミン白金錯体P
t(NH3)2(NO2)2水溶液を含浸させ、大気中で120
℃×2時間の乾燥を行い、さらに大気中で500℃×2
時間の熱処理を行って、CeO2-ZrO2粉末にPtを
担持した。この方法においてジニトロジアンミン白金錯
体水溶液の含浸量を変化させ、Pt/CeO2-ZrO2
の質量比が、0.5/95.5、1/99、2/98、3
/97の4通りの排気ガス浄化用触媒を得た。
Comparative Example 1 CeO 2 -ZrO 2 powder was added to dinitrodiammine platinum complex P
It is impregnated with an aqueous solution of t (NH 3 ) 2 (NO 2 ) 2 and then exposed to 120
Dry at ℃ × 2 hours, and further in the air at 500 ℃ × 2
The Pt was supported on the CeO 2 —ZrO 2 powder by heat treatment for a period of time. In this method, the impregnation amount of the dinitrodiammine platinum complex aqueous solution was changed to obtain Pt / CeO 2 -ZrO 2
Mass ratio of 0.5 / 95.5, 1/99, 2/98, 3
Four types of exhaust gas purification catalysts of / 97 were obtained.

【0030】−触媒性能の評価− 上記の実施例と比較例の各触媒をそれぞれ圧縮・解砕
し、直径約1〜3mmのペレット状の触媒に成形した
後、大気雰囲気中で800℃×3時間の耐久処理に供し
た。
-Evaluation of Catalyst Performance- Each of the catalysts of the above Examples and Comparative Examples was compressed and crushed to form a pellet-shaped catalyst having a diameter of about 1 to 3 mm, and then 800 ° C x 3 in an air atmosphere. It was subjected to a time endurance treatment.

【0031】これら耐久処理後の触媒の各2.0gを、
実験室用の排気ガス浄化性能評価装置の反応管内部に設
置し、下記に示す組成のモデルガス(ストイキ排気ガス
相当)を流通させ、触媒床温度を10℃/分の速度で降
温させながら、C36の50%浄化温度(T50)を測定し
た。このモデルガスの流量は6.0リットル/分/0.0
15g担持金属量(Pt+W又はMo)とした。 0.20%CO+667ppmC36+0.4%O2(残余N
2) このようにして測定された各触媒のT50を図2にまとめ
て示す。
2.0 g of each of the catalysts after the endurance treatment,
It is installed inside the reaction tube of an exhaust gas purification performance evaluation device for a laboratory, a model gas (corresponding to stoichiometric exhaust gas) having the composition shown below is circulated, and the catalyst bed temperature is lowered at a rate of 10 ° C / min. It was measured 50% purification temperature (T50) of C 3 H 6. The flow rate of this model gas is 6.0 l / min / 0.0
The amount of supported metal was 15 g (Pt + W or Mo). 0.20% CO + 667ppmC 3 H 6 + 0.4% O 2 ( remainder N
2 ) The T50 of each catalyst thus measured is shown in FIG.

【0032】図2に示した結果から、Pt/W又はMo
の質量比を7/3として、W粒子の上にPtを担持した
実施例1の各触媒、及びMo粒子の上にPtを担持した
実施例2の各触媒と、CeO2-ZrO2にPtを直接担
持した比較例1の各触媒のT50を比較すると、実施例1
の(Pt+W)の担持量、実施例2の(Pt+Mo)の担持
量、及び比較例1のPt担持量が同等なときに、実施例
1と実施例2は、比較例1を若干上回る浄化性能(T50
がやや低い)を示すことが分かる。したがって、W又は
Moの担持量に相当する量のPtを削減しても、同等以
上の浄化性能が得られることが分かる。
From the results shown in FIG. 2, Pt / W or Mo
Of Pt on W particles and each catalyst of Example 2 on which Pt was supported on Mo particles, and Pt on CeO 2 —ZrO 2 at a mass ratio of 7/3. Comparing T50 of each catalyst of Comparative Example 1 directly supporting
When the carried amount of (Pt + W), the carried amount of (Pt + Mo) of Example 2, and the carried amount of Pt of Comparative Example 1 are the same, Example 1 and Example 2 show slightly higher purification performance than Comparative Example 1. (T50
Is slightly lower). Therefore, it can be seen that even if the amount of Pt corresponding to the amount of W or Mo supported is reduced, the same or higher purification performance can be obtained.

【0033】−各触媒の形態観察− 上記の実施例と比較例の各触媒について、耐久処理の前
後で、透過型電子顕微鏡(TEM)による形態観察と、エ
ネルギー分散型X線分光分析(EDX)による電子顕微鏡
像のスポット領域における元素分析を行った。
-Observation of Morphology of Each Catalyst- For each catalyst of the above-mentioned Examples and Comparative Examples, morphological observation by a transmission electron microscope (TEM) and energy dispersive X-ray spectroscopy (EDX) before and after durability treatment. Elemental analysis was carried out in the spot region of the electron microscope image by.

【0034】耐久処理の前では、実施例1の各触媒はい
ずれも、TEM像からは金属粒子が2〜10nmの直径
を有することが観察された。また、Ptは、分解能約1
nmのEDXにおいても単独のPt粒子としては観察さ
れなかったが、各金属粒子からはPtとWが同時に検出
され、端部に向かうにつれてPtの濃度が高くなる様子
から、PtはW粒子の上にのみ存在するものと判断され
た。
Before the durability treatment, it was observed from the TEM image that each of the catalysts of Example 1 had metal particles having a diameter of 2 to 10 nm. Also, Pt has a resolution of about 1
Although it was not observed as a single Pt particle even in EDX of nm, Pt and W were detected at the same time from each metal particle, and the concentration of Pt increases toward the edge. Was determined to exist only in.

【0035】同様に、実施例2の耐久処理前の各触媒は
いずれも、Mo粒子が2〜10nmの直径を有すること
が観察され、また、PtはMo粒子の上にのみ存在する
ものと判断された。また、耐久処理後の実施例1〜2の
各触媒は、W又はMoとPtの存在形態に耐久処理前と
で有意な変化が観察されなかった。
Similarly, in each of the catalysts of Example 2 before endurance treatment, it was observed that the Mo particles had a diameter of 2 to 10 nm, and it was judged that Pt was present only on the Mo particles. Was done. Further, in each of the catalysts of Examples 1 and 2 after the durability treatment, no significant change was observed in the existing forms of W or Mo and Pt before the durability treatment.

【0036】一方、比較例1の各触媒は、耐久処理前は
分解能約1nmのEDXにおいても単独のPt粒子とし
ては観察されず、CeO2-ZrO2粒子の上に全体的に
存在することが観察されたが、耐久処理後では、Ptは
直径約20〜30nmの粒子に成長していることが観察
された。
On the other hand, each catalyst of Comparative Example 1 was not observed as a single Pt particle even in the EDX having a resolution of about 1 nm before the endurance treatment, and could be entirely present on the CeO 2 -ZrO 2 particle. Although observed, Pt was observed to grow into particles having a diameter of about 20 to 30 nm after the durability treatment.

【0037】[0037]

【発明の効果】貴金属の担持量が削減され、かつシンタ
リングが抑制された排気ガス浄化用触媒を提供すること
ができる。
EFFECT OF THE INVENTION It is possible to provide an exhaust gas purifying catalyst in which the amount of noble metal carried is reduced and sintering is suppressed.

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

【図1】本発明の排気ガス浄化用触媒のモデル図であ
る。
FIG. 1 is a model diagram of an exhaust gas purifying catalyst of the present invention.

【図2】大気雰囲気中800℃×3時間の耐久処理後の
36の50%浄化温度を比較したグラフである。
FIG. 2 is a graph comparing 50% purification temperatures of C 3 H 6 after endurance treatment at 800 ° C. for 3 hours in an air atmosphere.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01J 37/16 B01D 53/36 104Z F01N 3/10 ZAB Fターム(参考) 3G091 AA02 AB01 BA39 GB01X GB05W GB10X 4D048 AA13 AA18 BA08X BA19X BA26X BA27X BA30X BA31Y BA32Y BA33Y BA34Y BA41X BB01 BB17 4G069 AA03 AA08 BA05B BB02A BB02B BB04A BB04B BC32A BC33A BC43B BC59A BC59B BC60A BC60B BC69A BC75B CA03 CA14 CA15 EB18Y EB19 EC28 FA01 FA02 FB14 FB19 FB45 FC08 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) B01J 37/16 B01D 53/36 104Z F01N 3/10 ZAB F term (reference) 3G091 AA02 AB01 BA39 GB01X GB05W GB10X 4D048 AA13 AA18 BA08X BA19X BA26X BA27X BA30X BA31Y BA32Y BA33Y BA34Y BA41X BB01 BB17 4G069 AA03 AA08 BA05B BB02A BB02B BB04A BB04B BC32A BC33A BC45A EC4519 CA45BCAB19CA15BCA19B14BCAB14CA14BBC19B14CA14A

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 W又はMoの少なくとも一方の金属粒子
が酸化物担体に担持され、前記金属粒子の上に貴金属が
担持されたことを特徴とする排気ガス浄化用触媒。
1. An exhaust gas purifying catalyst, wherein at least one metal particle of W or Mo is supported on an oxide carrier, and a noble metal is supported on the metal particle.
【請求項2】 前記金属粒子が1〜15nmの直径を有
する請求項1に記載の排気ガス浄化用触媒。
2. The exhaust gas purifying catalyst according to claim 1, wherein the metal particles have a diameter of 1 to 15 nm.
【請求項3】 前記貴金属/前記金属粒子の質量比が1
〜10である請求項1又は2に記載の排気ガス浄化用触
媒。
3. The noble metal / metal particle mass ratio is 1
The exhaust gas purifying catalyst according to claim 1 or 2, which is 10 to 10.
【請求項4】 酸化物担体に担持されたW又はMoの少
なくとも一方の金属粒子の上に貴金属を還元析出させる
ことを特徴とする請求項1〜3のいずれか1項に記載の
排気ガス浄化用触媒の製造方法。
4. The exhaust gas purification according to claim 1, wherein the noble metal is reduced and deposited on the metal particles of at least one of W and Mo supported on the oxide carrier. For producing catalyst for automobile.
JP2002100157A 2002-04-02 2002-04-02 Catalyst for cleaning exhaust gas and manufacture method therefor Pending JP2003290658A (en)

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US7713911B2 (en) 2004-03-23 2010-05-11 Nissan Motor Co., Ltd. Catalyst powder, exhaust gas purifying catalyst, and method of producing the catalyst powder
US7674744B2 (en) 2004-03-31 2010-03-09 Nissan Motor Co., Ltd. Catalyst powder, method of producing the catalyst powder, and exhaust gas purifying catalyst
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US9364792B2 (en) 2006-08-25 2016-06-14 Tokyo Roki Co., Ltd. Catalyst, method and apparatus for removing nitrogen oxide
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