JP2001198463A - Catalyst for exhaust-gas purification - Google Patents

Catalyst for exhaust-gas purification

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Publication number
JP2001198463A
JP2001198463A JP2000014090A JP2000014090A JP2001198463A JP 2001198463 A JP2001198463 A JP 2001198463A JP 2000014090 A JP2000014090 A JP 2000014090A JP 2000014090 A JP2000014090 A JP 2000014090A JP 2001198463 A JP2001198463 A JP 2001198463A
Authority
JP
Japan
Prior art keywords
catalyst
nox
exhaust gas
storage material
carrier
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
JP2000014090A
Other languages
Japanese (ja)
Inventor
Masahiko Takeuchi
雅彦 竹内
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 JP2000014090A priority Critical patent/JP2001198463A/en
Publication of JP2001198463A publication Critical patent/JP2001198463A/en
Pending legal-status Critical Current

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  • Catalysts (AREA)
  • Exhaust Gas After Treatment (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To produce a catalyst for exhaust-gas purification superior in the heat resistance, by providing an NOx-occlusion substance for repeating the stable absorption-desorption of NOx even at a high temperature. SOLUTION: This catalyst carries as an NOx-occlusion substance an inorganic compound having a chemical structure reversibly changeable consequently upon NOx absorption on the lean side and NOx desorption on the rich side, and in the catalyst K2WO4, KtaO3, or KVO3 is carried as the NOx-occlusion substance. The NOx-occlusion substance is carried preferably on a carrier comprising alumina, titania, silica, silica-alumina, zirconia, zeolite, ceria, or a mixture thereof, and further a catalytic metal comprising Pt, Pd, Au, Ag, Ph, Ir or a mixture thereof is carried on the carrier.

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、自動車などの内燃
機関から排出される排気ガスを浄化するための排気ガス
浄化用触媒に関し、より詳しくは、高温下で優れたNO
X 浄化性能を呈するNOX 吸蔵還元型の排気ガス浄化用
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 for purifying exhaust gas emitted from an internal combustion engine of an automobile or the like, and more particularly, to an excellent NOx catalyst at high temperatures.
It relates the NO X storage-reduction type exhaust gas purifying catalyst exhibiting X purification performance.

【0002】[0002]

【従来の技術】近年、地球保護の観点より、自動車等の
内燃機関から排出される二酸化炭素(CO2 )の総量を
抑えること、NOX の発生量を抑えることが世界的な課
題となり、排気ガス規制及び燃費規制が年々強化されつ
つある。この対応策として、燃費向上の目的でリーンバ
ーンエンジンが開発され、その排気ガスを浄化する目的
で、従来の三元触媒にリーン側でNOX を吸蔵する機能
を付加させたNOX 吸蔵還元型三元触媒が開発され、上
記課題に対して一定の成功を収めている。
In recent years, from the viewpoint of global protection, to suppress the total amount of carbon dioxide (CO 2) discharged from an internal combustion engine such as an automobile, it is a global issue of suppressing the generation amount of NO X, the exhaust Gas regulations and fuel economy regulations are being strengthened year by year. As a countermeasure, a lean-burn engine has been developed for the purpose of improving fuel economy, the purpose of purifying the exhaust gas, NO X storage reduction obtained by adding a function of occluding NO X in the lean side to the conventional three-way catalyst Three-way catalysts have been developed and have achieved some success with the above issues.

【0003】このリーンバーンエンジンは、燃料を、常
時は空燃比(A/F)がリーン(空気過剰)の条件下で
燃焼させ、一時的にストイキ(理論空燃比)〜リッチ
(燃料過剰)の条件下で燃焼させる。排気ガス中のHC
(炭化水素類)やCOは、リーン側で酸化性雰囲気と触
媒の作用により効率的に燃焼除去され、一方、NOX
リーン側では吸蔵材に吸収され、それが一時的なストイ
キ〜リッチ条件下において放出され、その一時的還元性
雰囲気と触媒の作用により還元浄化される。
[0003] In this lean burn engine, fuel is normally burned under the condition that the air-fuel ratio (A / F) is lean (excess air), and the fuel is temporarily stoichiometric (stoichiometric air-fuel ratio) to rich (excess fuel). Burn under conditions. HC in exhaust gas
(Hydrocarbons) and CO are efficiently burned and removed by the action of an oxidizing atmosphere and the catalyst in the lean side, whereas, NO X is in the lean side is absorbed by the occluding material, it temporary stoichiometric-rich condition It is released under the atmosphere and is reduced and purified by the action of the catalyst and its temporary reducing atmosphere.

【0004】これらの空燃比制御とNOX 吸蔵型三元触
媒の作用により、全体として、燃費を向上させると同時
に排気ガス中のHC、CO、NOX を効率よく浄化する
ことができる。NOX 吸蔵材としては、特開平9−24
8458号公報、特開平10−33984号公報、特開
平10−128114号公報等に記載されているよう
に、各種のアルカリ金属やアルカリ土類金属の炭酸塩や
酢酸塩等が提案され、なかでも酢酸カリウムが良好であ
ることが見出されている。
[0004] By the action of these air-fuel ratio control and the NO X storage type three-way catalyst, as a whole, HC simultaneously exhaust gas when improving the fuel economy, CO, can be purified efficiently NO X. As the NO X storage material, JP-A-9-24
As described in JP-A No. 8458, JP-A-10-33984, JP-A-10-128114, etc., carbonates and acetates of various alkali metals and alkaline earth metals have been proposed. Potassium acetate has been found to be good.

【0005】[0005]

【発明が解決しようとする課題】しかしながら、これら
の従来提案されたNOX 吸蔵材は、高温でのNOX 吸蔵
性能が不足し、例えば、酢酸カリウムは、排気ガス温度
が約500℃を下回る温度領域では良好なNOX 吸蔵性
能を発揮するものの、約500℃を超えるとNO X 吸蔵
性能が急激に低下するという問題がある。
SUMMARY OF THE INVENTION However, these
Previously proposed NOXThe storage material is NO at high temperatureXOcclusion
Lack of performance, for example, potassium acetate is
NO in the temperature range below about 500 ° CXOcclusion
Demonstrates performance, but NO above about 500 ° C XOcclusion
There is a problem that the performance is rapidly reduced.

【0006】これは以下の理由によるものであると考え
られる。即ち、酢酸カリウムは高温下で一旦炭酸カリウ
ムに変化する。この炭酸カリウムは、リーン側でNOX
と反応して硝酸塩を形成するが、ここでアニオン基の炭
酸基はガス状で逃散する。したがって、次いでリッチ側
で硝酸塩からNOX が放出されたときに、遊離したカリ
ウムカチオンは、もとの炭酸基と再結合することができ
ず、高温下でTiO2担体やコージエライト基材と直接
反応して強固に結合される。
This is considered to be due to the following reasons. That is, potassium acetate temporarily changes to potassium carbonate at a high temperature. This potassium carbonate is NO X on the lean side
Reacts with to form nitrates, where the carbonate groups of the anionic groups escape in gaseous form. Accordingly, then when the NO X is released from the nitrate in the rich side, free potassium cations can not recombine with the original carbonate groups, react directly with TiO 2 carrier and the cordierite substrate at a high temperature And are firmly connected.

【0007】したがって、本発明は、高温下でも安定に
NOX の吸放出を繰り返すことができるNOX 吸蔵材を
備え、耐熱性に優れた排気ガス浄化用触媒を提供するこ
とを目的とする。
Accordingly, the present invention is provided with the NO X storage material can be repeated absorbing and releasing stable NO X even at high temperatures, and to provide an excellent exhaust gas purifying catalyst in heat resistance.

【0008】[0008]

【課題を解決するための手段】上記目的は、リーン側で
のNOX 吸収とリッチ側でのNOX 放出に伴って化学構
造が可逆変化する無機化合物をNOX 吸蔵材として担持
し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。
Above object to an aspect of the feature that the chemical structure with the NO X emissions in NO X absorption and rich side of the lean side carrying an inorganic compound which reversibly changes as the NO X storage material And the exhaust gas purifying catalyst.

【0009】本発明でいう「可逆変化」とは、リーン側
でNOX が無機化合物のカチオン基と結合して無機化合
物のアニオン基が遊離し、次いでリッチ側でNOX とカ
チオン基の結合が切れたときに、これらのカチオン基と
アニオン基が再結合してもとの無機化合物の化学構造に
戻ることを意味する。言い換えると、酢酸カリウムのよ
うにアニオン基が変化したり逃散することなく、無機化
合物のカチオン基の結合の変化、及びアニオン基の遊離
と再結合が、排気ガス中のNOX を浄化する過程で繰り
返されることを意味する。具体的には、以降で説明する
耐熱性の促進試験としての「耐久熱処理」に供した後に
も、リッチ側でNOX を放出した状態で、最初に担持さ
れたときの化学構造の無機化合物が粉末X線回折分析等
によって同定されることを意味する。
In the present invention, the term "reversible change" means that on the lean side, NO X bonds to the cation group of the inorganic compound to release the anion group of the inorganic compound, and then, on the rich side, the bond between NO X and the cation group changes. It means that, when cut, these cation groups and anion groups are recombined to return to the chemical structure of the original inorganic compound. In other words, without escaping anionic groups may change as potassium acetate, a change in the binding of the cationic groups of the inorganic compound, and a free and recombination anionic groups, the process for purifying NO X in the exhaust gas Means to be repeated. Specifically, even after being subjected to "durable heat treatment" as an accelerated test of heat resistance described in the following, while releasing NO X in the rich side, the inorganic compound of chemical structure when it is first carried the It means that it is identified by powder X-ray diffraction analysis or the like.

【0010】また、上記目的は、K2 WO4 、KTaO
3 、又はKVO3 をNOX 吸蔵材として担持したことを
特徴とする排気ガス浄化用触媒によって達成される。吸
蔵材としてのK2 WO4 、KTaO3 、又はKVO
3 は、高温下でのNOX吸蔵性能に優れ、NOX の吸放
出を繰り返した後にも、もとの化学構造を維持すること
が見出されている。
[0010] The above-mentioned object is achieved by using K 2 WO 4 , KTaO
3 or KVO 3 is carried as an NO x storage material by an exhaust gas purifying catalyst. K 2 WO 4 , KTaO 3 or KVO as storage material
3 is excellent in the NO X storage performance at high temperatures, even after repeated absorption and desorption of NO X, have been found to maintain the original chemical structure.

【0011】[0011]

【発明の実施の形態】本発明は、リーン側でのNOX
収とリッチ側でのNOX 放出に伴って化学構造が可逆変
化する無機化合物をNOX 吸蔵材として担持したことを
特徴とする排気ガス浄化用触媒であり、このNOX 吸蔵
材としては、K2 WO4 、KTaO3、KVO3 、又は
これらの混合物が例示される。
DETAILED DESCRIPTION OF THE INVENTION The present invention has the chemical structure with the NO X emissions in NO X absorption and rich side of the lean side, characterized in that the carrying inorganic compound which reversibly changes as the NO X storage material It is an exhaust gas purifying catalyst, and examples of the NO X storage material include K 2 WO 4 , KTaO 3 , KVO 3 , and mixtures thereof.

【0012】かかるNOX 吸蔵材は、好ましくは、アル
ミナ、チタニア、シリカ、シリカ−アルミナ、ジルコニ
ア、ゼオライト、セリア、又はこれらの混合物からなる
担体の上に担持される。NOX 吸蔵材を担体上に担持す
る仕方としては、例えば、アルミナ等の担体粉末とNO
X 吸蔵材粉末を乾式又は湿式で混合し、必要により、乾
燥、焼成することによって行うことができる。
[0012] Such the NO X storage material, preferably alumina, titania, silica, silica - is carried alumina, zirconia, zeolite, on a carrier consisting of ceria, or mixtures thereof. As a method of supporting the NO X storage material on a carrier, for example, carrier powder such as alumina and NO
It can be performed by mixing the X occluding material powder in a dry or wet manner, and, if necessary, drying and firing.

【0013】K2 WO4 、KTaO3 、又はKVO3
担持量は、アルミナ等の担体の質量100gを基準に、
カリウム元素のモル数で0.01〜2モルが好ましく、
より好ましくは0.05〜0.5モルである。
The loading amount of K 2 WO 4 , KTaO 3 or KVO 3 is based on 100 g of a carrier such as alumina.
0.01 to 2 mol is preferable in terms of the number of moles of the potassium element,
More preferably, it is 0.05 to 0.5 mol.

【0014】好ましくは、上記の担体に、Pt、Pd、
Au、Ag、Ph、Ir、又はこれらの混合物からなる
触媒金属が担持される。かかる触媒金属の作用により、
排気ガス中のHCやCOの燃焼とNOX の吸放出が促進
されるためである。触媒金属を担持させるには、担体上
に金属粒子を堆積させることができる任意の方法から選
択される、例えば、沈殿法、吸着法、イオン交換法、還
元析出法等によって行うことができる。
Preferably, Pt, Pd,
A catalytic metal consisting of Au, Ag, Ph, Ir, or a mixture thereof is supported. By the action of such a catalytic metal,
This is because the absorption and desorption of combustion and NO X of HC and CO in the exhaust gas is promoted. The catalyst metal can be supported by a method selected from any methods capable of depositing metal particles on the support, such as a precipitation method, an adsorption method, an ion exchange method, and a reduction precipitation method.

【0015】触媒金属の担持量は、アルミナ等の担体の
質量100gを基準に、好ましくは0.1〜10g、よ
り好ましくは0.2〜2gである。
The amount of the supported catalyst metal is preferably 0.1 to 10 g, more preferably 0.2 to 2 g, based on 100 g of a carrier such as alumina.

【0016】このようにして担体上にNOX 吸蔵材と触
媒金属を備えた触媒は、一般的なモノリス型触媒として
使用する場合、モノリス基材上にその触媒を堆積させる
ことで実際の触媒として使用することができる。
[0016] Thus with the the NO X storage material and the catalytic metal on the support by the catalyst, when used as a general monolith catalysts, as actual catalyst by depositing the catalyst on the monolithic substrate Can be used.

【0017】[0017]

【実施例】実施例1 100gのAl2 3 、100gのTiO2 、及び4
8.9gのK2 WO4 の混合粉末を、500ccのイオン
交換水に分散させて撹拌し、ジニトロジアンミンPt硝
酸水溶液を2gPt相当量で添加し、1時間撹拌した
後、濾過・乾燥し、次いで大気雰囲気下の300℃で1
時間焼成し、触媒粉末Aを得た。
EXAMPLE 1 100 g Al 2 O 3 , 100 g TiO 2 , and 4 g
8.9 g of a mixed powder of K 2 WO 4 was dispersed in 500 cc of ion-exchanged water and stirred. An aqueous solution of dinitrodiammine Pt nitric acid was added in an amount of 2 g Pt, stirred for 1 hour, filtered, dried, and then dried. 1 at 300 ° C under air atmosphere
After calcination for a time, a catalyst powder A was obtained.

【0018】実施例2 K2 WO4 に代えて80.4gのKTaO3 を用いた以
外は実施例1と同様の方法で触媒粉末Bを得た。
Example 2 A catalyst powder B was obtained in the same manner as in Example 1 except that 80.4 g of KTaO 3 was used instead of K 2 WO 4 .

【0019】実施例3 K2 WO4 に代えて41.4gのKVO3 を用いた以外
は実施例1と同様の方法で触媒粉末Cを得た。
Example 3 A catalyst powder C was obtained in the same manner as in Example 1 except that 41.4 g of KVO 3 was used instead of K 2 WO 4 .

【0020】比較例1 K2 WO4 に代えて52.2gのK2 TiO3 を用いた
以外は実施例1と同様の方法で触媒粉末Dを得た。
Comparative Example 1 A catalyst powder D was obtained in the same manner as in Example 1 except that 52.2 g of K 2 TiO 3 was used instead of K 2 WO 4 .

【0021】比較例2 100gのAl2 3 、及び100gのTiO2 の混合
粉末を、500ccのイオン交換水に分散させて撹拌し、
ジニトロジアンミンPt硝酸水溶液を2gPt相当量で
添加し、1時間撹拌した後、濾過・乾燥し、次いで大気
雰囲気下の300℃で1時間焼成し、Pt担持酸化物を
得た。29.4gの酢酸カリウムを500ccのイオン交
換水に溶かした溶液に、このPt担持酸化物を分散さ
せ、加熱しながら撹拌して蒸発乾固させた後、500℃
で2時間焼成して触媒粉末Eを得た。
Comparative Example 2 A mixed powder of 100 g of Al 2 O 3 and 100 g of TiO 2 was dispersed in 500 cc of deionized water and stirred.
An aqueous solution of dinitrodiammine Pt nitric acid was added in an amount of 2 g Pt, and the mixture was stirred for 1 hour, filtered and dried, and then calcined at 300 ° C. for 1 hour in an air atmosphere to obtain a Pt-supported oxide. This Pt-supported oxide was dispersed in a solution in which 29.4 g of potassium acetate was dissolved in 500 cc of ion-exchanged water.
For 2 hours to obtain a catalyst powder E.

【0022】−耐久熱処理− 得られた触媒A〜Eを、それぞれ圧縮成形した後粉砕す
ることにより0.5〜1.7mmのサイズを有するペレッ
トにした。これらのペレット触媒を、800℃の下記の
リーンとリッチのモデルガス雰囲気にそれぞれ1分間と
4分間ずつ交互に合計で5時間暴露する耐久熱処理に供
した。 リッチガス組成: 500ppm NO+2000ppm HC+0.6%CO+1
0%CO2+0.3%O2 +200ppm SO2 +5%H
2 O(残余:N2 ) リーンガス組成: 500ppm NO+2000ppm HC+0.1%CO+1
0%CO2+6.5%O2 +200ppm SO2 +5%H
2 O(残余:N2
-Durable heat treatment- The obtained catalysts A to E were each compression-molded and then pulverized into pellets having a size of 0.5 to 1.7 mm. These pellet catalysts were subjected to a durable heat treatment in which they were alternately exposed to the following lean and rich model gas atmospheres at 800 ° C. for 1 minute and 4 minutes, respectively, for a total of 5 hours. Rich gas composition: 500ppm NO + 2000ppm HC + 0.6% CO + 1
0% CO 2 + 0.3% O 2 +200 ppm SO 2 + 5% H
2 O (residual: N 2 ) Lean gas composition: 500 ppm NO + 2000 ppm HC + 0.1% CO + 1
0% CO 2 + 6.5% O 2 +200 ppm SO 2 + 5% H
2 O (residual: N 2 )

【0023】−NOX 浄化性能− 上記の耐久熱処理後のペレット触媒A〜Eについて、上
記のリーンとリッチのモデルガス雰囲気にそれぞれ2分
間ずつ交互に切り替えた時のリーン雰囲気下の500℃
におけるNOX 浄化性能を測定し、下記の式によってN
X 浄化率を求めた。この結果を図1に示す。 NOX 浄化率=〔(入ガス濃度−出ガス濃度)÷入ガス
濃度〕×100
[0023] -NO X purification performance - for pellet catalyst A~E after the above endurance heat treatment, 500 ° C. under a lean atmosphere when switching alternatively 2 minutes each in model gas atmosphere of the lean and rich
Measuring the NO X purification performance in, N by the following equation
To determine the O X purification rate. The result is shown in FIG. NO X purification rate = [(inlet gas concentration - outlet gas concentration) ÷ inflow gas concentration] × 100

【0024】−カリウム化合物の同定− ペレット触媒A〜Eについて、上記の耐久熱処理の前後
で粉末X線回折分析によってカリウム化合物を同定し
た。この結果、触媒A〜Cについては、最初に担持した
2 WO4 等のみが検出され、化合物の化学構造に変化
がないことが確認された。一方、触媒Dからは、触媒作
成時に添加したK2 TiO3 のみが検出され、触媒Eか
らはカリウム化合物としてK2 TiO3 とK2 Ti2
5 が検出された。
-Identification of Potassium Compound- For the pellet catalysts A to E, potassium compounds were identified by powder X-ray diffraction analysis before and after the above-mentioned durability heat treatment. As a result, for the catalysts A to C, only K 2 WO 4 and the like initially supported were detected, and it was confirmed that there was no change in the chemical structure of the compound. On the other hand, from the catalyst D, only K 2 TiO 3 added at the time of preparing the catalyst was detected, and from the catalyst E, K 2 TiO 3 and K 2 Ti 2 O as potassium compounds were detected.
5 was detected.

【0025】上記の結果から、次のように考察される。
本発明による触媒A〜Cでは、800℃で5時間の耐久
熱処理の後でも、30%を上回るNOX 浄化率を示し、
かつNOX 吸蔵材の化学構造にも変化がなく、化学構造
の可逆変化によってNOX を吸放出したことが確認され
る。本発明のK2 WO4 等のNOX 吸蔵材は、リーン条
件下では、硝酸化合物を形成してカリウムイオンを遊離
するが、WO4 基、TaO3 基、VO3 基は移動性が極
めて低くかつ化学的に安定であることから、リッチ条件
下ではもとの場所で再度カリウムイオンと結合すること
ができ、したがって、化学構造は可逆的に変化すること
ができると考えられる。
From the above results, the following is considered.
In the catalyst A~C according to the invention, even after the endurance heat treatment for 5 hours at 800 ° C., shows the NO X purification rate of greater than 30%,
And the no change chemical structure of the NO X storage component that issued absorbing the NO X is confirmed by a reversible change in chemical structure. The NO X storage material such as K 2 WO 4 of the present invention forms a nitrate compound and releases potassium ions under lean conditions, but WO 4 , TaO 3 , and VO 3 groups have extremely low mobility. It is considered that the compound is chemically stable and can bind to the potassium ion again in the original place under the rich condition, and thus the chemical structure can be reversibly changed.

【0026】K2 TiO3 をNOX 吸蔵材として用いた
触媒Dでは、カリウムと酸素の結合が強固であってリー
ン条件下で切れないため、NOX は化学的に結合され
ず、NOX 吸蔵性能を発揮することができないものと考
えられる。なお、触媒Dでは、約5%と若干のNOX
化率が測定されているが、これは、チタン酸カリウムの
化学構造の変化に由来するものではなく、NOX とチタ
ン酸カリウムの単なるイオン的作用、又はNOX と担体
のAl2 3 もしくはTiO2 の作用によるものと考え
られる。
In the catalyst D using K 2 TiO 3 as the NO X storage material, the bond between potassium and oxygen is strong and cannot be cut off under lean conditions, so NO X is not chemically bonded and NO X storage is possible. It is considered that performance cannot be exhibited. In the catalyst D, a slight NO X purification rate of about 5% was measured, but this was not due to a change in the chemical structure of potassium titanate, but was caused by a simple ionization of NO X and potassium titanate. action, or believed to be due to Al 2 O 3 or the action of TiO 2 of the NO X and carrier.

【0027】また、NOX 吸蔵材として酢酸カリウムを
用いた触媒Eでは、20%を下回る本発明の触媒よりも
かなり低いNOX 浄化率が測定されているが、この理由
は、カリウムが担体のチタニアと反応してチタン酸カリ
ウムを形成したためと考えられる。
In the case of the catalyst E using potassium acetate as the NO X storage material, the NO X purification rate which was considerably lower than that of the catalyst of the present invention, which was less than 20%, was measured. It is considered that potassium titanate was formed by reacting with titania.

【0028】[0028]

【発明の効果】高温下でも安定にNOX の吸放出を繰り
返すことができる、耐熱性に優れた排気ガス浄化用触媒
を提供することができる。
Can be repeated absorbing and releasing stable in NO X at a high temperature according to the present invention, it is possible to provide an excellent exhaust gas purifying catalyst in heat resistance.

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

【図1】実施例と比較例の触媒について耐久熱処理後の
NOX 浄化性能を比較した図である。
1 is a graph comparing the NO X purification performance after endurance heat treatment for the catalyst of Examples and Comparative Examples.

───────────────────────────────────────────────────── 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) F01N 3/28 301 B01D 53/36 102B // B01J 20/04 102H B01J 23/64 103A Fターム(参考) 3G091 AA02 AA12 AA17 AB02 AB06 AB09 BA07 BA08 BA10 BA14 BA15 BA19 BA39 CB02 DA01 DA02 FB03 FB10 FB12 FC02 FC08 GA01 GA06 GA16 GB01W GB01X GB01Y GB02W GB02Y GB04X GB05W GB06W GB07W GB09X GB10W GB10X GB10Y GB16X HA08 HA18 4D048 AA06 AB02 AB07 BA03X BA07X BA15X BA23X BA24X BA27X BA41X BA42X BB01 EA04 4G066 AA13B AA20C AA24B AA25B AA28B CA28 DA02 FA12 FA22 GA06 GA16 4G069 AA03 BA01A BA01B BA04A BA04B BB02B BB06A BB06B BC03A BC03B BC54A BC54B BC56A BC56B BC60A BC60B BC75B CA03 CA08 CA13 EA02Y ED06 ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) F01N 3/28 301 B01D 53/36 102B // B01J 20/04 102H B01J 23/64 103A F-term (Reference) 3G091 AA02 AA12 AA17 AB02 AB06 AB09 BA07 BA08 BA10 BA14 BA15 BA19 BA39 CB02 DA01 DA02 FB03 FB10 FB12 FC02 FC08 GA01 GA06 GA16 GB01W GB01X GB01Y GB02W GB02Y GB04X GB05W GB06W GB07W GB09X BA10X GB10A GB18X10 BA10 BA27X BA41X BA42X BB01 EA04 4G066 AA13B AA20C AA24B AA25B AA28B CA28 DA02 FA12 FA22 GA06 GA16 4G069 AA03 BA01A BA01B BA04A BA04B BB02B BB06A BB06B BC03A BC03B BC54ABCBCBC BCBC BCBC BC BC BC BC BC BC BC BC BC BC BC BC BC BC BC BC BC BC BC BC

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 リーン側でのNOX 吸収とリッチ側での
NOX 放出に伴って化学構造が可逆変化する無機化合物
をNOX 吸蔵材として担持したことを特徴とする排気ガ
ス浄化用触媒。
1. An exhaust gas purifying catalyst characterized in that an inorganic compound whose chemical structure is reversibly changed as NO X is absorbed on the lean side and NO X is released on the rich side is supported as a NO X storage material.
【請求項2】 K2 WO4 、KTaO3 、又はKVO3
をNOX 吸蔵材として担持したことを特徴とする排気ガ
ス浄化用触媒。
2. K 2 WO 4 , KTaO 3 , or KVO 3
The exhaust gas purifying catalyst, characterized by carrying as the NO X storage material.
JP2000014090A 2000-01-19 2000-01-19 Catalyst for exhaust-gas purification Pending JP2001198463A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000014090A JP2001198463A (en) 2000-01-19 2000-01-19 Catalyst for exhaust-gas purification

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000014090A JP2001198463A (en) 2000-01-19 2000-01-19 Catalyst for exhaust-gas purification

Publications (1)

Publication Number Publication Date
JP2001198463A true JP2001198463A (en) 2001-07-24

Family

ID=18541596

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000014090A Pending JP2001198463A (en) 2000-01-19 2000-01-19 Catalyst for exhaust-gas purification

Country Status (1)

Country Link
JP (1) JP2001198463A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7338917B2 (en) 2004-03-30 2008-03-04 Honda Motor Co., Ltd. Purification catalyst for exhaust gas

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7338917B2 (en) 2004-03-30 2008-03-04 Honda Motor Co., Ltd. Purification catalyst for exhaust gas

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