JPH1176822A - Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides - Google Patents
Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxidesInfo
- Publication number
- JPH1176822A JPH1176822A JP9248326A JP24832697A JPH1176822A JP H1176822 A JPH1176822 A JP H1176822A JP 9248326 A JP9248326 A JP 9248326A JP 24832697 A JP24832697 A JP 24832697A JP H1176822 A JPH1176822 A JP H1176822A
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- JP
- Japan
- Prior art keywords
- nitrogen oxides
- exhaust gas
- removing nitrogen
- catalyst material
- spinel
- Prior art date
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Abstract
(57)【要約】
【課題】工場や発電所から排出される排気ガス、及び自
動車の希薄燃焼エンジンの排気ガス中に含まれる窒素酸
化物を、800℃の高温の酸化性雰囲気条件下でも還元
剤を用いることなく直接、窒素と酸素に分解除去可能な
触媒材料並びにそれを用いた窒素酸化物除去方法を提供
する。
【解決手段】MgとGaを主たる金属元素として含有す
るスピネル型結晶性複合酸化物に、該スピネル型結晶性
複合酸化物に対して0.5〜15.0重量%のPdと、
PdとAlの原子比(Pd/Al)が0.15〜1.0
の割合でAlを同時に担持して窒素酸化物除去用酸化物
触媒材料とし、該窒素酸化物除去用酸化物触媒材料を窒
素酸化物を含む排気ガスと接触させ、該排気ガスに含ま
れる窒素酸化物を還元剤を用いずに直接、窒素と酸素に
分解して除去する。(57) [Summary] [PROBLEMS] To reduce nitrogen oxides contained in exhaust gas discharged from a factory or a power plant and exhaust gas of a lean burn engine of an automobile even under a high-temperature oxidizing atmosphere condition of 800 ° C. Disclosed are a catalyst material which can be directly decomposed and removed into nitrogen and oxygen without using an agent, and a method for removing nitrogen oxides using the same. A spinel-type crystalline composite oxide containing Mg and Ga as main metal elements, Pd in an amount of 0.5 to 15.0% by weight based on the spinel-type crystalline composite oxide,
The atomic ratio of Pd to Al (Pd / Al) is 0.15 to 1.0
At the same time to form an oxide catalyst material for removing nitrogen oxides, bringing the oxide catalyst material for removing nitrogen oxides into contact with an exhaust gas containing nitrogen oxides, and removing nitrogen oxides contained in the exhaust gas. The substance is directly decomposed into nitrogen and oxygen without using a reducing agent and removed.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、定置式の工場の各
種工業炉や、発電所の内燃機関、及び移動式の自動車用
内燃機関等の各種排気ガス中に含まれる窒素酸化物を直
接、窒素と酸素に分解除去することが可能な酸化物触媒
材料並びにこれを用いて排気ガス中の窒素酸化物を還元
剤を用いずに直接、窒素と酸素に分解除去する方法に関
するもので、とりわけ排気ガス中の炭化水素濃度が低い
リーンバーンエンジン等の自動車排気ガス浄化用として
好適な窒素酸化物除去用酸化物触媒材料並びに該酸化物
触媒材料を用いて排気ガス中の窒素酸化物を直接、窒素
と酸素に分解して除去する方法に関するものである。BACKGROUND OF THE INVENTION The present invention relates to a method for directly converting nitrogen oxides contained in various exhaust gases from various industrial furnaces in stationary factories, internal combustion engines in power plants, and internal combustion engines for mobile vehicles. The present invention relates to an oxide catalyst material capable of being decomposed and removed into nitrogen and oxygen, and a method for directly decomposing and removing nitrogen oxides in exhaust gas into nitrogen and oxygen without using a reducing agent using the same. Oxide catalyst material for removing nitrogen oxides suitable for purifying automobile exhaust gas such as lean burn engines having a low hydrocarbon concentration in the gas and nitrogen oxides in the exhaust gas using the oxide catalyst material directly to form nitrogen gas And a method of decomposing and removing oxygen.
【0002】[0002]
【従来の技術】従来より、定置式の前記各種工業炉や内
燃機関および移動式の自動車に代表される内燃機関から
排出される排気ガス中に含まれる窒素酸化物は、人体に
悪影響を及ぼすだけでなく、酸性雨や光化学スモッグの
原因物質であるため、その大気中への放出は大きな環境
問題になっている。2. Description of the Related Art Conventionally, nitrogen oxides contained in exhaust gas discharged from various stationary industrial furnaces, internal combustion engines, and internal combustion engines typified by mobile vehicles have only adverse effects on human bodies. Rather, it is a substance that causes acid rain and photochemical smog, and its release into the atmosphere is a major environmental problem.
【0003】そこで、前記排気ガス中の窒素酸化物の除
去方法としては、かねてより主に接触還元法が用いられ
ており、例えば、前記工場及び発電所等の窒素酸化物の
固定発生源には、排気ガス中に多量の酸素を含むことか
ら、還元剤としてアンモニアを用い、バナジア(V2 O
5 )/チタニア(TiO2 )触媒により窒素酸化物を還
元除去している。Therefore, as a method of removing nitrogen oxides from the exhaust gas, a catalytic reduction method has been mainly used for a long time. For example, fixed sources of nitrogen oxides in the factories and power plants have been used. Since the exhaust gas contains a large amount of oxygen, ammonia is used as a reducing agent and vanadia (V 2 O
5 ) / Nitrogen oxides are reduced and removed by a titania (TiO 2 ) catalyst.
【0004】一方、自動車等の移動発生源には、排気ガ
ス中の酸素量が少ないため、該排気ガス中に残存する未
燃の一酸化炭素(CO)および炭化水素(CxHy)を
還元剤として用い、三元触媒により窒素酸化物を還元除
去しており、そのような方法に用いられる三元触媒とし
ては、Pd、Pt、Rh等の貴金属をγ−アルミナ(A
l2 O3 )で被覆したコージェライト等の耐火性担体に
担持したものが用いられていた。[0004] On the other hand, in mobile sources such as automobiles, since the amount of oxygen in the exhaust gas is small, unburned carbon monoxide (CO) and hydrocarbons (CxHy) remaining in the exhaust gas are used as reducing agents. Nitrogen oxide is reduced and removed by a three-way catalyst. As a three-way catalyst used in such a method, a noble metal such as Pd, Pt, Rh or the like is used in γ-alumina (A
(1 2 O 3 ), which is supported on a refractory carrier such as cordierite.
【0005】しかしながら、前記固定発生源の窒素酸化
物除去方法として用いられているアンモニアによる接触
還元法は、アンモニアが高価でかつ危険であり、取り扱
いに十分な注意が必要であるという理由から、移動発生
源には用いることができなかった。[0005] However, the catalytic reduction method using ammonia, which is used as a method for removing nitrogen oxides from the fixed source, is not suitable because ammonia is expensive and dangerous, and it requires careful handling. It could not be used as a source.
【0006】更に、自動車等の移動発生源においても、
現在、省エネルギー化のために注目されている希薄燃焼
エンジン(リーンバーンエンジン)では、排気ガス中の
未燃一酸化炭素及び炭化水素量が極端に少ないため、窒
素酸化物の還元作用を示さないという問題が残されてい
る。[0006] Further, in a mobile source such as an automobile,
At present, lean-burn engines (lean-burn engines), which have been attracting attention for energy saving, do not show a reduction effect of nitrogen oxides because the amounts of unburned carbon monoxide and hydrocarbons in exhaust gas are extremely small. The problem remains.
【0007】そこで、係る問題を解決するためには還元
剤を必要としない窒素酸化物の除去が最も簡単で理想的
であることから、還元剤を用いずに窒素酸化物を窒素と
酸素に直接分解する触媒の研究が種々行われており、こ
れまでに、銅イオン交換ゼオライト触媒を用いて400
〜500℃の温度範囲で窒素酸化物を窒素と酸素に直接
分解可能であること等が報告されている(特開平1−1
30735号公報、特開昭63−283727号公報参
照)。In order to solve the above problem, it is simplest and ideal to remove nitrogen oxides that do not require a reducing agent. Therefore, nitrogen oxides are directly converted into nitrogen and oxygen without using a reducing agent. Various studies have been conducted on decomposing catalysts. Until now, copper ion-exchanged zeolite catalysts have been used.
It has been reported that nitrogen oxides can be directly decomposed into nitrogen and oxygen in a temperature range of up to 500 ° C. (Japanese Patent Laid-Open No. 1-1).
No. 30735, JP-A-63-283727).
【0008】[0008]
【発明が解決しようとする課題】しかしながら、前記銅
イオン交換ゼオライト触媒を用いたものでは、600℃
を超えると窒素酸化物分解活性が急激に劣化してしまう
ことから、600℃を越える高温排気ガス条件下では、
窒素酸化物分解能力が低く、また、酸素が共存すると窒
素酸化物分解活性が著しく阻害されるため、実用上、使
用できないという課題があった。However, in the case of using the copper ion-exchanged zeolite catalyst, 600 ° C.
When the temperature exceeds 600 ° C., the nitrogen oxide decomposition activity rapidly deteriorates.
The nitrogen oxide decomposing ability is low, and the coexistence of oxygen significantly impairs the nitrogen oxide decomposing activity.
【0009】[0009]
【発明の目的】そこで、本発明は工場や発電所等の固定
発生源から排出される排気ガス、及び自動車等の移動発
生源、とりわけ希薄燃焼エンジン(リーンバーンエンジ
ン)等の酸素を含む排気ガス中に含まれる窒素酸化物
を、600℃を越える高温条件下でも還元剤を用いずに
直接、窒素と酸素に分解除去する触媒能を維持すること
ができる有用な触媒材料並びにそれを用いた窒素酸化物
除去方法を提供するものである。SUMMARY OF THE INVENTION Accordingly, the present invention relates to an exhaust gas emitted from a fixed source such as a factory or a power plant, and a mobile source such as an automobile, particularly an exhaust gas containing oxygen such as a lean burn engine (lean burn engine). A useful catalyst material capable of maintaining a catalytic ability to directly decompose and remove nitrogen oxides contained therein into nitrogen and oxygen without using a reducing agent even under high temperature conditions exceeding 600 ° C. and nitrogen using the same It is intended to provide an oxide removing method.
【0010】[0010]
【課題を解決するための手段】本発明は、前記課題に鑑
み成されたもので、Mg及びGaを主たる金属元素とし
て含有するスピネル型結晶性複合酸化物に、PdとAl
を同時に担持した触媒材料が、600℃を越える高温条
件下でも窒素酸化物の直接分解反応に高い活性を示し、
特に、希薄燃焼方式の内燃機関から排出される還元性ガ
スがほとんど存在しない窒素酸化物を含有する酸素含有
排気ガスにおいても、該排気ガス中の窒素酸化物を有効
に分解除去して浄化することができることを確認し、本
発明に至った。SUMMARY OF THE INVENTION The present invention has been made in view of the above-mentioned problems, and is directed to a spinel-type crystalline composite oxide containing Mg and Ga as main metal elements.
At the same time shows a high activity in the direct decomposition reaction of nitrogen oxides even under high temperature conditions exceeding 600 ° C.,
In particular, even in the case of an oxygen-containing exhaust gas containing nitrogen oxides, in which almost no reducing gas is discharged from a lean-burn internal combustion engine, it is necessary to purify the exhaust gas by effectively decomposing and removing the nitrogen oxides in the exhaust gas. It has been confirmed that the present invention can be performed, and the present invention has been achieved.
【0011】即ち、本発明の窒素酸化物除去用酸化物触
媒材料は、PdとAlを同時に担持した、MgとGaを
主たる金属元素として含有するスピネル型結晶性複合酸
化物で、Pdの担持量がスピネル型結晶性複合酸化物に
対して0.5〜15.0重量%で、AlがPdとAlの
原子比(Pd/Al)で0.15〜1.0の割合で担持
して成ることを特徴とするものである。That is, the oxide catalyst material for removing nitrogen oxides of the present invention is a spinel-type crystalline composite oxide containing Pd and Al at the same time and containing Mg and Ga as main metal elements. Is 0.5 to 15.0% by weight based on the spinel-type crystalline composite oxide, and Al is supported at a ratio of 0.15 to 1.0 in an atomic ratio of Pd to Al (Pd / Al). It is characterized by the following.
【0012】また、本発明の窒素酸化物除去方法は、P
dとAlを同時に担持した、MgとGaを主たる金属元
素として含有するスピネル型結晶性複合酸化物で、Pd
の担持量がスピネル型結晶性複合酸化物に対して0.5
〜15.0重量%で、AlがPdとAlの原子比(Pd
/Al)で0.15〜1.0の割合で担持した窒素酸化
物除去用酸化物触媒材料を用い、該触媒材料と窒素酸化
物を含む排気ガスを接触させ、還元剤を用いずに窒素酸
化物を窒素と酸素に直接分解することを特徴とするもの
である。Further, the method for removing nitrogen oxides according to the present invention
a spinel-type crystalline composite oxide containing Mg and Ga as the main metal elements that simultaneously supports
Is 0.5 to the spinel-type crystalline composite oxide.
15.0% by weight, Al is an atomic ratio of Pd to Al (Pd
/ Al) at a ratio of 0.15 to 1.0 using an oxide catalyst material for removing nitrogen oxides, contacting the catalyst material with an exhaust gas containing nitrogen oxides, and using a nitrogen gas without a reducing agent. The oxide is directly decomposed into nitrogen and oxygen.
【0013】[0013]
【作用】本発明の窒素酸化物除去用酸化物触媒材料並び
に窒素酸化物除去方法によれば、本発明の窒素酸化物除
去用酸化物触媒材料は、MgとGaを主たる金属元素と
して含有するスピネル型結晶性複合酸化物にPdとAl
を担持し、Pdの担持量がスピネル型結晶性複合酸化物
に対して0.5〜15.0重量%、AlをPdとAlの
原子比(Pd/Al)で0.15〜1.0の割合とした
ことから、同時に担持したアルミニウム化合物がPdの
電子状態を変化させた結果、Pdの酸化を抑制し、ま
た、窒素酸化物との親和性が向上し、高い窒素酸化物分
解活性が発現することになる。According to the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention, the oxide catalyst material for removing nitrogen oxides of the present invention comprises a spinel containing Mg and Ga as main metal elements. Pd and Al
And the loading amount of Pd is 0.5 to 15.0% by weight based on the spinel-type crystalline composite oxide, and Al is contained in an atomic ratio of Pd to Al (Pd / Al) of 0.15 to 1.0%. As a result, the aluminum compound supported simultaneously changes the electronic state of Pd, thereby suppressing the oxidation of Pd, improving the affinity with nitrogen oxide, and increasing the nitrogen oxide decomposition activity. Will be expressed.
【0014】[0014]
【発明の実施の形態】以下、本発明の窒素酸化物除去用
酸化物触媒材料並びに窒素酸化物除去方法を詳細に説明
する。BEST MODE FOR CARRYING OUT THE INVENTION The oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides according to the present invention will be described in detail below.
【0015】本発明において、窒素酸化物除去用酸化物
触媒材料としてスピネル型結晶性複合酸化物に担持する
Pdの量は、該スピネル型結晶性複合酸化物に対して
0.5重量%未満の場合には、触媒活性がほとんど発現
せず、逆に、15.0重量%を越えると触媒活性の向上
効果が認められないことから、0.5〜15.0重量%
に特定され、特に触媒活性の点から前記担持量は1.0
〜10.0重量%がより好ましく、更に3.0〜7.0
重量%が最も望ましい傾向を示す。In the present invention, the amount of Pd supported on the spinel-type crystalline composite oxide as an oxide catalyst material for removing nitrogen oxides is less than 0.5% by weight based on the spinel-type crystalline composite oxide. In this case, the catalyst activity is hardly exhibited. On the contrary, if it exceeds 15.0% by weight, no improvement effect of the catalyst activity is recognized.
In particular, from the viewpoint of catalytic activity, the supported amount is 1.0
To 10.0% by weight, more preferably 3.0 to 7.0% by weight.
% By weight indicates the most desirable trend.
【0016】また、前記スピネル型結晶性複合酸化物に
添加するアルミニウム化合物は、PdとAlの原子比
(Pd/Al)の割合が0.15より小さくなるとアル
ミニウム化合物添加による触媒活性の向上効果が認めら
れず、逆に1.0を超えると、Pdの耐酸化性がほとん
ど改善されないことから、Pd/Alは0.15〜1.
0に特定され、特に触媒活性の点からは0.2〜0.5
の添加量がより好ましく、更に0.25〜0.3の添加
量が最も望ましい傾向を示す。When the ratio of the atomic ratio of Pd to Al (Pd / Al) is less than 0.15, the effect of improving the catalytic activity of the aluminum compound added to the spinel-type crystalline composite oxide is reduced. On the contrary, if it exceeds 1.0, the oxidation resistance of Pd is hardly improved, so that Pd / Al is 0.15 to 1.0.
0, and especially from 0.2 to 0.5 in terms of catalytic activity.
Is more preferable, and the addition amount of 0.25 to 0.3 shows the most desirable tendency.
【0017】また、前記スピネル型結晶性複合酸化物
は、窒素酸化物を含有する還元ガスが存在しない模擬排
気ガスと接触させると、該模擬排気ガス中の窒素酸化物
を窒素と酸素に直接分解する優れた特性を有することが
認められる。When the spinel-type crystalline composite oxide is brought into contact with a simulated exhaust gas containing no reducing gas containing nitrogen oxide, the nitrogen oxide in the simulated exhaust gas is directly decomposed into nitrogen and oxygen. It is recognized that it has excellent properties.
【0018】尚、前記複合酸化物は、主たる金属元素と
してMgとGaを含有し、Ga/Mgの原子比nが2.
5〜3.3の比率から成るスピネル型結晶性複合酸化物
であり、MgGan O4+z (但し、n=2.5〜3.
3)の一般式で表されるものであり、前記式中の(O
4+z )は複合酸化物として安定に存在するために必要な
酸素量であり、該酸素量は前記nの値により0.2以下
の範囲で随時変化するものである。The composite oxide contains Mg and Ga as main metal elements, and has an atomic ratio n of Ga / Mg of 2.
A spinel crystalline composite oxide consisting of the ratio of 5~3.3, MgGa n O 4 + z ( where, n = 2.5 to 3.
Represented by the general formula 3), wherein (O)
4 + z ) is the amount of oxygen necessary to exist stably as a composite oxide, and the amount of oxygen changes as needed in the range of 0.2 or less depending on the value of n.
【0019】また、本発明で用いられる複合酸化物は、
Ga/Mg原子比nの値が2.5〜3.3の範囲を逸脱
すると触媒活性が低下するため、前記範囲に特定され、
とりわけ2.8〜3.0が最も望ましい。The composite oxide used in the present invention is:
If the value of the Ga / Mg atomic ratio n deviates from the range of 2.5 to 3.3, the catalytic activity decreases.
Particularly, 2.8 to 3.0 is most desirable.
【0020】次に、本発明の窒素酸化物除去用酸化物触
媒材料の製造方法について一例を詳述する。Next, an example of the method for producing the oxide catalyst material for removing nitrogen oxides of the present invention will be described in detail.
【0021】本発明の複合酸化物は、Mg及びGaを含
有する原料粉末を、Ga/Mgの原子比nが2.5〜
3.3の範囲内となるように秤量し、十分に撹袢混合し
た後、酸化性雰囲気中、500〜1600℃の温度で5
〜30時間熱処理することにより、金属元素としてMg
及びGaを含有するスピネル型結晶を主結晶相とする複
合酸化物粉末が得られる。The composite oxide of the present invention is obtained by mixing a raw material powder containing Mg and Ga with an atomic ratio n of Ga / Mg of 2.5 to 2.5.
After being weighed so as to fall within the range of 3.3 and sufficiently stirred and mixed, the mixture is heated in a oxidizing atmosphere at a temperature of 500 to 1600 ° C. for 5 minutes.
Heat treatment for up to 30 hours, Mg as a metal element
And a composite oxide powder having a spinel type crystal containing Ga as a main crystal phase.
【0022】前記原料粉末としては、例えば、Mg及び
Gaの酸化物や、熱処理により酸化物を生成するそれら
の炭酸塩、硝酸塩、酢酸塩等を用いることができる。As the raw material powder, for example, Mg and Ga oxides, and their carbonates, nitrates, acetates, etc., which form oxides by heat treatment, can be used.
【0023】また前記複合酸化物は、前記以外に酸化物
や他の金属塩による固相反応法や、金属アルコキシド等
のゾル−ゲル法等によっても合成できるものであり、何
等これら製造方法に限定されるものではない。In addition, the composite oxide can be synthesized by a solid phase reaction method using an oxide or another metal salt, or a sol-gel method such as a metal alkoxide. It is not something to be done.
【0024】前記製造方法において、いずれも熱処理
は、該熱処理温度が500℃より低いと結晶化が不十分
となり、逆に1600℃を越えると緻密化してしまうた
め、500〜1600℃の温度で、酸化性雰囲気中、5
〜30時間行うが、特に低い温度で熱処理することが粉
末の比表面積を高める上で有効であり、実用的には、比
表面積が35m2 /g以上となるように設定することが
望ましい。In any of the above-mentioned manufacturing methods, in any of the heat treatments, if the heat treatment temperature is lower than 500 ° C., crystallization becomes insufficient, and if the heat treatment temperature exceeds 1600 ° C., densification occurs. In an oxidizing atmosphere, 5
Heat treatment at a low temperature is effective for increasing the specific surface area of the powder, and practically, it is desirable to set the specific surface area to 35 m 2 / g or more.
【0025】次に、かくして得られた前記複合酸化物を
担持体としてPdとAlを担持するが、その担持方法は
特に限定されるものではなく、蒸発乾固法や含浸法等の
公知の方法が適用でき、例えば、前記所定量のPdを含
有する溶液と前記所定原子比のAlを含有する溶液を前
記担持体粉末に添加した後、蒸発乾固し、ヘリウム(H
e)ガス等の雰囲気中、400〜600℃の温度で3〜
5時間熱処理することにより、本発明のPdとAlを担
持したMg−Ga系スピネル型結晶性複合酸化物から成
る窒素酸化物除去用酸化物触媒材料が得られる。Next, Pd and Al are supported on the composite oxide thus obtained as a support. The method for supporting Pd and Al is not particularly limited, and known methods such as an evaporation to dryness method and an impregnation method are used. For example, a solution containing the predetermined amount of Pd and a solution containing Al at the predetermined atomic ratio are added to the carrier powder, and then evaporated to dryness, and helium (H
e) in an atmosphere of gas or the like at a temperature of 400 to 600 ° C.
By performing the heat treatment for 5 hours, the oxide catalyst material for removing nitrogen oxides comprising the Mg—Ga-based spinel-type crystalline composite oxide supporting Pd and Al according to the present invention is obtained.
【0026】尚、前記Pd及びAlの溶液調製に用いる
Pd及びAlの塩は、特に限定されるものではないが、
通常、その硝酸塩類、硫酸塩類、炭酸塩類、塩酸、ハロ
ゲン化物等の各種無機塩類、酢酸塩等の有機塩類、水酸
化物や酸化物等が挙げられる。The salt of Pd and Al used for preparing the solution of Pd and Al is not particularly limited.
Usually, various inorganic salts such as nitrates, sulfates, carbonates, hydrochloric acid, halides and the like, organic salts such as acetates, hydroxides and oxides and the like can be mentioned.
【0027】また、前記Pd及びAlの塩を溶液にする
に際して用いる溶媒は、水あるいはアルコール、カルボ
ニル化合物等の有機物が好適に用いられる。As the solvent used for preparing the Pd and Al salts into a solution, water or an organic substance such as an alcohol or a carbonyl compound is preferably used.
【0028】次に、前記熱処理の雰囲気は特に制限はな
いが、通常、He、N2 、アルゴン(Ar)等の不活性
ガス、または不活性ガスによる水素の希釈ガス等も用い
ることができる。Next, the atmosphere of the heat treatment is not particularly limited, but an inert gas such as He, N 2 , argon (Ar) or a diluting gas of hydrogen with an inert gas can be used.
【0029】更に、前記熱処理温度における処理時間も
特に限定されるものではなく、通常3〜5時間で充分で
あり、また、熱処理中に温度を段階的に変化させること
も可能である。Further, the treatment time at the above-mentioned heat treatment temperature is not particularly limited, and usually 3 to 5 hours is sufficient, and the temperature can be changed stepwise during the heat treatment.
【0030】かくして得られた触媒材料は、窒素酸化物
を含む排気ガスに接触させることにより、還元剤を用い
ることなく窒素酸化物を窒素と酸素に直接分解すること
が可能となる。By contacting the catalyst material thus obtained with an exhaust gas containing nitrogen oxides, the nitrogen oxides can be directly decomposed into nitrogen and oxygen without using a reducing agent.
【0031】[0031]
【実施例】次に、本発明を評価するに際し、出発原料と
してMg(NO3 )2 ・6H2 O、及びGa(NO3 )
2 ・9H2 Oの試薬を用い、MgとGaの金属比が1対
3の割合となるように秤量し、これらの試薬を蒸留水中
に溶解させ、撹拌しながらアンモニア水で中和し、この
時に生成した沈殿物を濾過、洗浄し、凍結乾燥させた。EXAMPLES In evaluating the present invention, Mg (NO 3 ) 2 .6H 2 O and Ga (NO 3 ) were used as starting materials.
Using reagents 2 · 9H 2 O, metal ratio of Mg and Ga were weighed so that a ratio of 1: 3, dissolved the reagents in distilled water, neutralized with aqueous ammonia while stirring, the The precipitate formed at times was filtered, washed and lyophilized.
【0032】かくして得られた乾燥粉末を大気中、70
0℃の温度で30時間、熱処理して比表面積が40〜5
0m2 /gのスピネル型結晶性複合酸化物粉末を作製し
た。The dry powder thus obtained is placed in air at 70
Heat treatment at 0 ° C. for 30 hours for specific surface area of 40-5
A spinel-type crystalline composite oxide powder of 0 m 2 / g was produced.
【0033】その後、前記スピネル型複合酸化物粉末に
Pd及びAlの担持量が表1に示す割合となるようにP
dとAl含有水溶液を添加して蒸発乾固後、熱処理して
PdとAlを担持したスピネル型結晶性複合酸化物粉末
を得た。Thereafter, Pd and Al were loaded on the spinel-type composite oxide powder so that the loading amounts of Pd and Al were as shown in Table 1.
An aqueous solution containing d and Al was added, evaporated to dryness, and then heat-treated to obtain a spinel-type crystalline composite oxide powder supporting Pd and Al.
【0034】次いで、前記PdとAlを担持したスピネ
ル型結晶性複合酸化物粉末を金型プレスにより成形し、
更に冷間静水圧成形法により圧縮してから該成形物を解
砕して篩別し、500μmを越え、700μm以下に整
粒して評価用の触媒試料を調製した。Next, the spinel-type crystalline composite oxide powder supporting Pd and Al is molded by a mold press.
Further, after being compressed by a cold isostatic pressing method, the molded product was crushed and sieved, and sized to a size exceeding 500 μm and not more than 700 μm to prepare a catalyst sample for evaluation.
【0035】尚、前記PdとAlを全く担持しないスピ
ネル型結晶性複合酸化物触媒のみの触媒活性、及び銅イ
オン交換ゼオライトの触媒活性を比較例とした。Incidentally, the catalytic activity of only the spinel-type crystalline composite oxide catalyst not supporting Pd and Al at all and the catalytic activity of copper ion-exchanged zeolite were used as comparative examples.
【0036】次いで、模擬排気ガスとして窒素酸化物で
あるNOが3000ppm、残部がHeから成る反応ガ
スを、該反応ガスと触媒材料が接触する条件として、空
間速度(SV)を9000/hr.に設定して前記評価
用の触媒試料を充填した触媒層に流し、600〜800
℃の温度範囲で触媒層を通過して生成したN2 ガスをガ
スクロマトグラフで測定した。Next, as a simulated exhaust gas, a space gas (SV) of 9000 / hr was used as a condition for contacting the catalyst material with the reaction gas consisting of 3000 ppm of NO as nitrogen oxide and the balance of He. And flowed through the catalyst layer filled with the catalyst sample for evaluation.
N 2 gas generated through the catalyst layer in a temperature range of ° C. was measured by gas chromatography.
【0037】触媒のNO分解能は、触媒層出口側のN2
濃度(ppm)の2倍の値を、触媒層入口側のNO濃度
(ppm)で除した百分率をNO除去率(%)とし、各
温度でのNO除去率を求めると共に、本発明による効果
を明確にするために、800℃の温度におけるO2 が2
%存在する模擬排気ガスでのNO除去率も求めた。The NO resolution of the catalyst is determined by the N 2 at the outlet of the catalyst layer.
The NO removal rate (%) is obtained by dividing the value twice the concentration (ppm) by the NO concentration (ppm) on the catalyst layer inlet side, and the NO removal rate at each temperature is obtained. For clarity, O 2 at a temperature of 800 ° C. is 2
The NO removal rate in the simulated exhaust gas containing% was also determined.
【0038】その結果から、O2 が存在しない場合の前
記測定温度が600℃の温度を越える領域で前記測定温
度におけるNO除去率の最大値が20%を越え、かつ、
800℃の温度におけるO2 存在下でのNO除去率が5
%以上となるものを良と総合評価した。The results show that the maximum value of the NO removal rate at the measurement temperature exceeds 20% in a region where the measurement temperature in the absence of O 2 exceeds 600 ° C., and
NO removal rate in the presence of O 2 at a temperature of 800 ° C. is 5
% Or more was evaluated as good.
【0039】[0039]
【表1】 [Table 1]
【0040】表から明らかなように、比較例である試料
番号18及び19ではいずれも600℃を越える高温度
域ではO2 の存在の有無を問わずNOの分解活性が極め
て低く、また本発明の請求範囲外である試料番号1、9
ではO2 の存在の有無を問わずNO分解活性が低く、同
じく試料番号10、16、17ではいずれもO2 存在下
でのNO分解活性が全体的に低く実用的でないことが明
らかとなった。As is clear from the table, in Sample Nos. 18 and 19, which are comparative examples, NO decomposition activity was extremely low in the high temperature range exceeding 600 ° C. regardless of the presence or absence of O 2. Sample Nos. 1 and 9 outside the scope of claims
Shows that the NO decomposition activity is low irrespective of the presence or absence of O 2 , and it was also found that the NO decomposition activity in the presence of O 2 was low for all samples Nos. 10, 16 and 17, which were not practical. .
【0041】それに対して、本発明ではいずれも800
℃という高温の酸化性雰囲気下でも十分なNO分解活性
を示していることが分かる。On the other hand, in the present invention, 800
It can be seen that sufficient NO decomposition activity is exhibited even in an oxidizing atmosphere at a high temperature of ° C.
【0042】[0042]
【発明の効果】以上、詳述したように本発明の窒素酸化
物除去用酸化物触媒材料並びに窒素酸化物除去方法によ
れば、該酸化物触媒材料はMgとGaを主たる金属元素
として含有するスピネル型結晶性複合酸化物に、0.5
〜15.0重量%のPdと、PdとAlの原子比(Pd
/Al)が0.15〜1.0の割合から成るAlとを同
時に担持したものであり、前記酸化物触媒材料と窒素酸
化物を含有する還元ガスが存在しない排気ガスとを接触
させることにより、800℃の高温の酸化性雰囲気下で
も、窒素酸化物が窒素と酸素に直接分解され、600℃
を越える高温度域まで十分な窒素酸化物分解活性能力を
有していることから、工場や発電所等の固定発生源は勿
論、自動車等の移動発生源からの排気ガス中に含まれる
窒素酸化物をも有効に直接分解除去することができる。As described above, according to the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention, the oxide catalyst material contains Mg and Ga as main metal elements. 0.5 to the spinel-type crystalline composite oxide
~ 15.0% by weight of Pd and the atomic ratio of Pd to Al (Pd
/ Al) at the same time carrying Al having a ratio of 0.15 to 1.0, and contacting the oxide catalyst material with an exhaust gas containing no nitrogen oxide-containing reducing gas. Nitrogen oxides are directly decomposed into nitrogen and oxygen even under a high temperature oxidizing atmosphere of
It has a sufficient activity to decompose nitrogen oxides up to a high temperature range, which is higher than the temperature range above, so that nitrogen oxides contained in exhaust gas from mobile sources such as automobiles as well as stationary sources such as factories and power plants The object can also be directly decomposed and removed effectively.
【0043】その結果、省エネルギー、省資源及び地球
温暖化防止を目標として開発される今後のリーンバーン
エンジン等の各種内燃機関の排気ガスをはじめ、窒素酸
化物を含有する各種有害物質の浄化に極めて有用なもの
となる。As a result, it is extremely useful for purifying various harmful substances containing nitrogen oxides, including exhaust gas of various internal combustion engines such as lean burn engines which will be developed with the aim of saving energy and resources and preventing global warming. It will be useful.
Claims (2)
を主たる金属元素として含有するスピネル型結晶性複合
酸化物に、パラジウム(Pd)とアルミニウム(Al)
を前記スピネル型結晶性複合酸化物に対してパラジウム
(Pd)が0.5〜15.0重量%、アルミニウム(A
l)がパラジウム(Pd)とアルミニウム(Al)の原
子比(Pd/Al)で0.15〜1.0の割合で担持し
て成ることを特徴とする窒素酸化物除去用酸化物触媒材
料。1. Magnesium (Mg) and gallium (Ga)
(Pd) and aluminum (Al) in spinel-type crystalline composite oxides containing
Is 0.5 to 15.0% by weight of palladium (Pd) based on the spinel-type crystalline composite oxide and aluminum (A
1) An oxide catalyst material for removing nitrogen oxides, characterized in that l) is supported at an atomic ratio (Pd / Al) of palladium (Pd) and aluminum (Al) of 0.15 to 1.0.
を主たる金属元素として含有するスピネル型結晶性複合
酸化物に、パラジウム(Pd)とアルミニウム(Al)
を前記スピネル型結晶性複合酸化物に対してパラジウム
(Pd)が0.5〜15.0重量%、アルミニウム(A
l)がパラジウム(Pd)とアルミニウム(Al)の原
子比(Pd/Al)で0.15〜1.0の割合で担持し
て成る窒素酸化物除去用酸化物触媒材料を、窒素酸化物
を含む排気ガスと接触させ、該窒素酸化物を直接、窒素
と酸素に分解することを特徴とする窒素酸化物除去方
法。2. Magnesium (Mg) and gallium (Ga)
(Pd) and aluminum (Al) in spinel-type crystalline composite oxides containing
Is 0.5 to 15.0% by weight of palladium (Pd) based on the spinel-type crystalline composite oxide and aluminum (A
l) is an oxide catalyst material for removing nitrogen oxide, which is supported at an atomic ratio (Pd / Al) of palladium (Pd) and aluminum (Al) of 0.15 to 1.0, A method for removing nitrogen oxides, which comprises contacting an exhaust gas containing the nitrogen oxides to directly decompose the nitrogen oxides into nitrogen and oxygen.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9248326A JPH1176822A (en) | 1997-09-12 | 1997-09-12 | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9248326A JPH1176822A (en) | 1997-09-12 | 1997-09-12 | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH1176822A true JPH1176822A (en) | 1999-03-23 |
Family
ID=17176424
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9248326A Pending JPH1176822A (en) | 1997-09-12 | 1997-09-12 | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH1176822A (en) |
-
1997
- 1997-09-12 JP JP9248326A patent/JPH1176822A/en active Pending
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