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JPH08150337A - Oxide catalyst material for removing nitrogen oxide and method for removing nitrogen oxide - Google Patents

Oxide catalyst material for removing nitrogen oxide and method for removing nitrogen oxide

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Publication number
JPH08150337A
JPH08150337A JP6294255A JP29425594A JPH08150337A JP H08150337 A JPH08150337 A JP H08150337A JP 6294255 A JP6294255 A JP 6294255A JP 29425594 A JP29425594 A JP 29425594A JP H08150337 A JPH08150337 A JP H08150337A
Authority
JP
Japan
Prior art keywords
exhaust gas
oxide
nitrogen oxides
catalyst material
removing nitrogen
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
JP6294255A
Other languages
Japanese (ja)
Other versions
JP3309024B2 (en
Inventor
Masaharu Nonoguchi
正治 野々口
Hitoshi Matsunosako
等 松之迫
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.)
Kyocera Corp
Original Assignee
Kyocera 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
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Priority to JP29425594A priority Critical patent/JP3309024B2/en
Publication of JPH08150337A publication Critical patent/JPH08150337A/en
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Publication of JP3309024B2 publication Critical patent/JP3309024B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Abstract

(57)【要約】 【目的】水蒸気存在下は勿論、高酸素濃度雰囲気下、W
/F値が高くても、高いNOX 還元分解作用を有し、省
エネルギー、省資源用として開発中の各種内燃機関の排
気ガスをはじめ、NOX を含有する各種有害物質の浄化
に有用である。 【構成】窒素酸化物除去用酸化物触媒材料として、Ni
とGaを主金属元素として含有する主結晶相がスピネル
型構造の複合酸化物とアルミナを混合して成り、高濃度
の酸素が存在し、かつ炭化水素等の還元性ガスが存在す
る酸化雰囲気中で、窒素酸化物を含む排気ガスと接触さ
せて窒素酸化物を還元分解し除去する。
(57) [Summary] [Purpose] Not only in the presence of water vapor, but also in a high oxygen concentration atmosphere, W
Even if the / F value is high, it has a high NO X reductive decomposition action and is useful for purification of various harmful substances containing NO X , including exhaust gas of various internal combustion engines under development for energy saving and resource saving. . [Structure] Ni as an oxide catalyst material for removing nitrogen oxides
In an oxidizing atmosphere in which the main crystal phase containing Al and Ga as the main metal element is a mixture of a complex oxide having a spinel structure and alumina, in which a high concentration of oxygen exists and a reducing gas such as hydrocarbon exists. Then, the exhaust gas containing nitrogen oxides is brought into contact with the exhaust gas to reduce and decompose the nitrogen oxides.

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、窒素酸化物を還元除去
することのできる新規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除去する方法に関するも
のである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a novel oxide catalyst material capable of reducing and removing nitrogen oxides and a method for removing nitrogen oxides in exhaust gas using the same.

【0002】[0002]

【従来技術】近年、各種汚染物質による大気の汚れが大
きな社会問題となり、その中でも大気汚染の移動発生源
となっている自動車の排気ガス中のNOX 、COX 等の
有害物質を分解、除去する方法の開発が急務となってい
る。
BACKGROUND ART In recent years, contamination of the atmosphere by various pollutants is a major social problem, NO X in the exhaust gas of an automobile that is the moving source of air pollution among them, decompose harmful substances such as CO X, removed There is an urgent need to develop ways to do it.

【0003】従来より自動車の排気ガス中のNOX 、C
X 等の有害物質を分解、除去する方法として、一酸化
炭素(CO)及び炭化水素(CX X )の酸化と、窒素
酸化物(NOX )の還元を同時に行う三元触媒を用いる
方法が採用されてきた。
Conventionally, NO x , C in the exhaust gas of automobiles
Decomposing harmful substances O X such as a method of removing, using an oxidation of carbon monoxide (CO) and hydrocarbons (C X H X), nitrogen oxide three-way catalyst to perform reduction at the same time the (NO X) The method has been adopted.

【0004】そのような方法に用いられる三元触媒とし
ては、パラジウム(Pd)、白金(Pt)、ロジウム
(Rh)等の貴金属を、γ−アルミナ(Al2 3 )で
被覆したコージェライト等の耐火物に担持したものが用
いられていた。
As a three-way catalyst used in such a method, cordierite obtained by coating a noble metal such as palladium (Pd), platinum (Pt) or rhodium (Rh) with γ-alumina (Al 2 O 3 ) is used. What was carried on the refractory of was used.

【0005】しかしながら、前記三元触媒は、およそ
0.5%程度の低酸素濃度においてのみ排気ガスの浄化
を効率よく行うことができ、排気ガスの酸素濃度が1%
を越えるような高濃度域では有効に働かなくなるという
欠点がある。
However, the three-way catalyst can efficiently purify the exhaust gas only at a low oxygen concentration of about 0.5%, and the oxygen concentration of the exhaust gas is 1%.
It has a drawback that it does not work effectively in a high concentration range exceeding the range.

【0006】そこで、通常は排気ガス中の酸素濃度を測
定し、CO及びCX X 、NOX を高い浄化率で処理し
得る理論等量値に近い範囲の空燃比となるように制御す
ることが行われているが、前記CO及びCX X と、N
X の発生メカニズムが相反する特性を有するため、限
られた状態での燃焼を維持しなければならず、それより
高い酸素濃度中での排気ガス浄化はほとんどできていな
いのが現状である。
Therefore, normally, the oxygen concentration in the exhaust gas is measured, and the air-fuel ratio is controlled so that CO, C X H X , and NO X can be processed at a high purification rate, and the air-fuel ratio is in a range close to the theoretical equivalent value. However, the CO and C X H X , and N
Since O X generation mechanisms have contradictory properties, it is necessary to support combustion in a state where limited exhaust gas purification at a high oxygen concentration in than it is at present, not hardly.

【0007】更に、昨今、省エネルギー、省資源も叫ば
れていることから、ガソリンエンジンにおいては、低燃
費化を図るために希薄燃焼方式の研究開発が行われてい
るが、この場合、排気ガス中の酸素濃度は数%と高くな
り、触媒の貴金属が酸素被毒により排気ガスの浄化がで
きなくなるという欠点がある。
Further, since energy saving and resource saving have recently been demanded, in a gasoline engine, research and development of a lean combustion system have been carried out in order to achieve low fuel consumption. Has a disadvantage that the noble metal of the catalyst cannot be purified by exhaust gas due to oxygen poisoning.

【0008】またディーゼルエンジンにおいても、現在
の燃焼方式では排気ガス中の酸素濃度が高いために排気
ガスの浄化が全くなされていないのが現状である。
Also in the diesel engine, in the present combustion system, the exhaust gas is not purified at all because the oxygen concentration in the exhaust gas is high.

【0009】一方、約1000℃以上の高温で発生し、
燃焼温度が高くなるほどその濃度が高くなるNOX を効
果的に浄化する方法としては、前記以外にアンモニアを
用いた選択的接触還元法があるが、工場等の固定式の燃
焼装置における酸素濃度の高い排気ガス中のNOX の浄
化に対しては有効ではあるものの、本方法を自動車等の
移動式燃焼装置に適用することは安全性の面で問題があ
る。
On the other hand, it occurs at a high temperature of about 1000 ° C. or higher,
As a method of effectively purifying NO X , the concentration of which increases as the combustion temperature increases, there is a selective catalytic reduction method using ammonia in addition to the above method. Although effective for purifying NO x in high exhaust gas, applying this method to a mobile combustion device such as an automobile has a problem in safety.

【0010】そこで、前記諸問題を解消するものとし
て、金属を担持した疎水性ゼオライトを触媒として炭化
水素と接触させながらNOX を除去する方法が、特開平
4−349938号公報等に提案されている。
[0010] Therefore, as to solve the above problems, a method of the hydrophobic zeolite carrying the metal removing NO X while in contact with the hydrocarbon as a catalyst, is proposed in JP-A 4-349938 Patent Publication There is.

【0011】[0011]

【発明が解決しようとする課題】しかしながら、前記金
属を担持した疎水性ゼオライトを触媒とするものは耐水
性が悪く、ディーゼルエンジンのように排気ガス中に水
分を含むような場合には水蒸気の存在によりNOX の浄
化率の経時低下が大きく、その用途が限定されるという
課題があり、耐熱性だけではなく耐水性にも優れた触媒
材料が望まれていた。
However, the one using the above-mentioned metal-supporting hydrophobic zeolite as a catalyst has poor water resistance, and in the case where the exhaust gas contains water as in a diesel engine, the presence of water vapor is present. Therefore, there is a problem that the purification rate of NO X is greatly decreased with time and its use is limited, and a catalyst material excellent in not only heat resistance but also water resistance has been desired.

【0012】[0012]

【発明の目的】本発明はアンモニア等の毒性の強い還元
剤を必要とせず、ディーゼルエンジン等の水分を含む酸
素濃度の高い排気ガスを、該排気ガスの流速が高速度で
あっても、有効に排気ガス中のNOX を浄化することが
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。
OBJECT OF THE INVENTION The present invention does not require a highly toxic reducing agent such as ammonia, and is effective for exhaust gas with high oxygen concentration containing moisture such as diesel engine even if the flow speed of the exhaust gas is high. The present invention also provides a useful catalyst material that can purify NO x in exhaust gas and a method for removing nitrogen oxides using the catalyst material.

【0013】[0013]

【課題を解決するための手段】本発明は、上記課題に鑑
みなされたもので、NiおよびGaを主たる金属元素と
して含有する結晶相がスピネル型構造である複合酸化物
に、Al2 3 を混合した酸化物触媒材料が、水蒸気存
在下の高い酸素濃度でも優れた触媒活性を長期にわたり
有することを見出したものである。
The present invention has been made in view of the above problems, and Al 2 O 3 is added to a complex oxide having a spinel structure as a crystal phase containing Ni and Ga as main metal elements. It has been found that the mixed oxide catalyst material has excellent catalytic activity for a long period of time even at high oxygen concentration in the presence of water vapor.

【0014】即ち、本発明の窒素酸化物除去用酸化物触
媒材料は、NiおよびGaを主たる金属元素として含有
し、その結晶相がスピネル型構造を有する複合酸化物粉
末と、Al2 3 粉末を混合して成る触媒材料である。
That is, the oxide catalyst material for removing nitrogen oxides of the present invention contains a composite oxide powder containing Ni and Ga as main metal elements, and the crystal phase of which has a spinel type structure, and Al 2 O 3 powder. Is a catalyst material formed by mixing

【0015】更に、本発明の窒素酸化物除去方法は、高
濃度の酸素と還元性を有する炭素含有ガスが存在する酸
化雰囲気中で、Ni及びGaを主たる金属元素として含
有する結晶相がスピネル型構造である複合酸化物に、A
2 3 を混合した触媒材料と、窒素酸化物を含む排気
ガスを接触させることを特徴とするものである。
Further, according to the method for removing nitrogen oxides of the present invention, the crystal phase containing Ni and Ga as main metal elements is spinel type in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present. The structure of the complex oxide, A
It is characterized in that a catalyst material mixed with l 2 O 3 is brought into contact with an exhaust gas containing nitrogen oxides.

【0016】本発明において、前記複合酸化物は、Ni
及びGaを主たる金属元素として含有し、一般式として
NiGa2 4 で表されるスピネル型構造の結晶相を有
するものであり、該複合酸化物のNiとGaの相関は、
Niに対するGaの蛍光X線分析によるカウント比で論
ずると、触媒活性の点からは1.4以上がより望まし
く、とりわけ1.5以上であれば最も好ましい。
In the present invention, the composite oxide is Ni
And Ga as main metal elements and has a crystal phase of spinel structure represented by NiGa 2 O 4 as a general formula, and the correlation between Ni and Ga of the composite oxide is
In terms of the count ratio of Ga to Ni by fluorescent X-ray analysis, 1.4 or more is more desirable from the viewpoint of catalytic activity, and most preferably 1.5 or more.

【0017】また、前記Al2 3 は高い比表面積を有
するものが適当であると考えられ、実用的には60m2
/g以上が望ましく、また、Al2 3 混合量による触
媒活性の変化は少ないものの、その混合量は20〜70
重量%が好ましく、25〜60重量%が最も望ましい。
Further, it is considered that the Al 2 O 3 having a high specific surface area is suitable, and 60 m 2 is practically used.
/ G or more is desirable, and although the change in catalyst activity due to the Al 2 O 3 mixed amount is small, the mixed amount is 20 to 70.
Weight percent is preferred and 25-60 weight percent is most desirable.

【0018】更に、前記複合酸化物にAl2 3 を混合
した触媒材料と、窒素酸化物を含む排気ガスを接触させ
る際、該排気ガス雰囲気中に、還元剤としてC2 4
36 、C3 8 等の炭化水素、CH3 OH、C2
5 OH等のアルコール、CO等の還元性を有する炭素ガ
ス等を含有させて、前記触媒材料と接触させると、NO
X 還元性が一層高くなる。
Further, when the catalyst material obtained by mixing the composite oxide with Al 2 O 3 and the exhaust gas containing nitrogen oxide are brought into contact with each other, C 2 H 4 as a reducing agent in the exhaust gas atmosphere,
Hydrocarbons such as C 3 H 6 and C 3 H 8 , CH 3 OH, C 2 H
When an alcohol such as 5 OH or the like, a carbon gas having a reducing property such as CO or the like is contained and brought into contact with the catalyst material, NO
X- reducing property becomes higher.

【0019】[0019]

【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、酸化物触媒材料は、N
i及びGaを主たる金属元素として含有し、結晶相がス
ピネル型構造を有する複合酸化物と、Al2 3 を混合
したものであることから、触媒材料中のAl2 3 がN
Oを酸化してNO2 の生成を促進し、NOよりNO2
対する還元活性の方が高いNi−Ga系酸化物触媒によ
って、NOX の還元分解作用で高い特性を示す。
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 is N
i and Ga contained as the main metal element, a complex oxide crystal phase having a spinel structure, since it is a mixture of Al 2 O 3, Al 2 O 3 in the catalyst material is N
Oxidation of O promotes the generation of NO 2 , and the Ni—Ga-based oxide catalyst, which has a higher reduction activity for NO 2 than NO, exhibits high characteristics due to the reductive decomposition action of NO X.

【0020】[0020]

【実施例】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について、実施例に基づ
き詳細に述べる。
EXAMPLES Hereinafter, the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention will be described in detail based on examples.

【0021】本発明の窒素酸化物除去用酸化物触媒材料
の製造方法は、先ず、Ni及びGaを含有する原料粉末
を所定量秤量し、十分に攪拌混合した後、Al2 3
末を添加し、酸化雰囲気中、500〜1600℃の温度
で5〜30時間熱処理することにより、Ni及びGaを
主たる金属元素とするスピネル型結晶の複合酸化物とA
2 3 から成る混合粉末が得られる。
In the method for producing an oxide catalyst material for removing nitrogen oxides according to the present invention, first, a predetermined amount of a raw material powder containing Ni and Ga is weighed, sufficiently stirred and mixed, and then Al 2 O 3 powder is added. Then, by heat-treating at a temperature of 500 to 1600 ° C. for 5 to 30 hours in an oxidizing atmosphere, a composite oxide of spinel type crystals containing Ni and Ga as main metal elements and A
A mixed powder of 1 2 O 3 is obtained.

【0022】前記原料粉末としては、例えば、Ni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, oxides of Ni and Ga, and their carbonates, nitrates, acetates and the like which produce oxides by heat treatment can be used.

【0023】また、前記原料粉末は、定比のスピネル型
構造を示すNiGa2 4 にGa金属を固溶することに
よりNOX の還元分解特性が向上すると考えられること
から、Niに対するGaの金属元素比が2.1以上にな
るように配合することが望ましい。
Further, since it is considered that the raw material powder improves the reductive decomposition property of NO x by solid-dissolving Ga metal in NiGa 2 O 4 having a stoichiometric spinel structure, the metal of Ga with respect to Ni is It is desirable to mix them so that the element ratio is 2.1 or more.

【0024】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や、金属アルコキシド等の
ゾル−ゲル法等により合成できるものであり、何等これ
らの製造方法に限定されるものではない。
In addition to the above, the complex oxide can be synthesized by a solid-state reaction with an oxide or another metal salt, a sol-gel method using a metal alkoxide or the like, and is not limited to any production method thereof. Not something.

【0025】前記製造方法において、いずれも熱処理
は、熱処理温度が500℃より低いと結晶化が不充分と
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ために有効であり、実用的には、比
表面積が60m2 /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, if the heat treatment temperature is lower than 500 ° C., the crystallization becomes insufficient, and if the heat treatment temperature exceeds 1600 ° C., densification occurs. Therefore, oxidation is performed at a temperature of 500 to 1600 ° C. 5 in the atmosphere
It is carried out for 30 hours, but heat treatment at a particularly low temperature is effective for increasing the specific surface area of the powder, and in practice, it is desirable to set the specific surface area to be 60 m 2 / g or more.

【0026】次に、本発明を評価するに際し、出発原料
としてNi(NO3 2 ・6H2 OとGa(NO3 3
・9H2 Oの試薬を用い、NiとGaの金属元素比が
1:3となるように秤量し、これら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、
生成した沈澱物の泥漿100重量部にAl2 3 の粉末
を、25〜75重量部添加し、超音波乳化分散機で十分
に攪拌混合した後、これを凍結乾燥させた。
Next, in evaluating the present invention, Ni (NO 3 ) 2 .6H 2 O and Ga (NO 3 ) 3 were used as starting materials.
-Using a reagent of 9H 2 O, weighed so that the metal element ratio of Ni and Ga was 1: 3, dissolved these reagents in distilled water, and neutralized with ammonia water while stirring.
25 to 75 parts by weight of Al 2 O 3 powder was added to 100 parts by weight of the formed precipitate slurry, and the mixture was sufficiently stirred and mixed by an ultrasonic emulsification disperser, and then freeze-dried.

【0027】次に、該乾燥粉末を大気中、700℃の温
度で30時間、熱処理して酸化物触媒粉末を調製し、該
粉末を金型プレスにより成形後、CIP成形し、該成形
体を解砕して篩別し、500μmを越え、700μm以
下に整粒して評価用試料を調製した。
Next, the dry powder is heat-treated in the air at a temperature of 700 ° C. for 30 hours to prepare an oxide catalyst powder, which is molded by a die press and then CIP molded to obtain the molded body. The sample was crushed, sieved, and sized to exceed 500 μm and 700 μm or less to prepare a sample for evaluation.

【0028】尚、Al2 3 を混合しないものを前記同
様に調製して比較例とした。
Incidentally, a material not mixed with Al 2 O 3 was prepared in the same manner as the above and used as a comparative example.

【0029】かくして得られた評価用材料の粉末を用い
て蛍光X線分析により求めたNiに対するGaのカウン
ト比は、1.93であった。
The count ratio of Ga to Ni determined by fluorescent X-ray analysis using the powder of the evaluation material thus obtained was 1.93.

【0030】また、X線回折測定(XRD)により結晶
相を同定し、結晶相がスピネル結晶とγ−Al2 3
からなることを確認した。
The crystal phase was identified by X-ray diffraction measurement (XRD), and it was confirmed that the crystal phase consisted of a spinel crystal and a γ-Al 2 O 3 phase.

【0031】次いで、NOが1000ppm、O2 が5
%又は10%、H2 Oが10%、還元剤としてC2 4
が1000ppm又はC3 6 が666ppm、残部が
Heから成る水蒸気を含有した反応ガスを、該反応ガス
と触媒材料が接触する条件として、W/Fを0.03g
・sec/ccに設定し、前記評価用材料を充填した触
媒層に流し、300〜600℃の温度範囲でNOの還元
により生成したN2 をガスクロマトグラフで測定し、N
2 の生成量から最高活性を示す450℃のNO転換率を
NO還元活性として評価した。
Next, NO 1000 ppm and O 2 5
% Or 10%, H 2 O 10%, C 2 H 4 as reducing agent
Is 1000 ppm or C 3 H 6 is 666 ppm, and the balance is a reaction gas containing water vapor consisting of He, and W / F is 0.03 g as a condition for contacting the reaction gas with the catalyst material.
Set to sec / cc, flow through the catalyst layer filled with the evaluation material, and measure N 2 produced by NO reduction in the temperature range of 300 to 600 ° C. by gas chromatograph.
The NO conversion rate at 450 ° C., which shows the highest activity, was evaluated as the NO reduction activity from the production amount of 2 .

【0032】[0032]

【表1】 [Table 1]

【0033】表1から明らかなように、Al2 3 を混
合しない比較例である試料番号1、5、11及び15
は、いずれも450℃におけるNO還元活性が33%以
下であるのに対して、本発明では450℃におけるNO
還元活性が35%以上を示していることが分かる。
As is clear from Table 1, sample numbers 1, 5, 11 and 15 which are comparative examples in which Al 2 O 3 is not mixed.
Has a NO reduction activity at 450 ° C. of 33% or less, whereas in the present invention, NO at 450 ° C.
It can be seen that the reducing activity shows 35% or more.

【0034】また、前記評価用の複合酸化物を使用し、
4気筒のディーゼルエンジン台上試験装置の排気管にセ
ットし、該ディーゼルエンジンを最高回転数、全負荷の
条件で100時間運転する耐久試験を実施し、試験後の
複合酸化物について前記同様にしてNO還元活性を評価
したが、NO転換率はほとんど低下していないことが確
認でき、耐水性に優れていることも証明された。
Further, using the above-mentioned composite oxide for evaluation,
A four-cylinder diesel engine bench test device was set on the exhaust pipe, and a durability test was conducted in which the diesel engine was operated for 100 hours at maximum rotation speed and full load. The NO reduction activity was evaluated, but it was confirmed that the NO conversion rate was hardly reduced, and it was also proved that the water resistance was excellent.

【0035】[0035]

【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NiとGaを主たる金属元素
として含有するスピネル型構造の複合酸化物に、Al2
3 を混合したものであることから、水蒸気が存在する
雰囲気中は勿論、排気ガス中の酸素濃度が3%以上の高
酸素濃度雰囲気下であっても、その上、ガスの流速が高
速度であっても、優れたNOX 還元性能を有することか
ら、排気ガス中に含まれるNOX を有効に還元除去する
ことができ、省エネルギー、省資源を目標として開発さ
れる今後のディーゼルエンジンや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、NOX を含有す
る各種有害物質の浄化に極めて有用なものである。
As described above in detail, 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 Ni and Ga as main metal elements. Al 2 is added to the complex oxide of spinel structure.
Since it is a mixture of O 3 , the flow velocity of the gas is high even when the oxygen concentration in the exhaust gas is 3% or more in the high oxygen concentration atmosphere as well as in the atmosphere in which water vapor exists. However, since it has excellent NO X reduction performance, it can effectively reduce and remove NO X contained in exhaust gas, and future diesel engines and lean engines developed with the goal of energy saving and resource saving. It is extremely useful for purifying various harmful substances containing NO x , including exhaust gas from various internal combustion engines such as a burn engine.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/36 102 C 102 H ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Office reference number FI technical display location B01D 53/36 102 C 102 H

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】少なくともニッケル(Ni)とガリウム
(Ga)を主たる金属元素として含有するスピネル型構
造の複合酸化物に、アルミナ(Al2 3 )を混合した
ことを特徴とする窒素酸化物除去用酸化物触媒材料。
1. Nitrogen oxide removal characterized by mixing alumina (Al 2 O 3 ) with a composite oxide having a spinel structure containing at least nickel (Ni) and gallium (Ga) as main metal elements. Oxide catalyst material.
【請求項2】高濃度の酸素と還元性を有する炭素含有ガ
スが存在する酸化雰囲気中で、少なくともニッケル(N
i)とガリウム(Ga)を主たる金属元素として含有す
るスピネル型構造の複合酸化物に、アルミナ(Al2
3 )を混合して成る酸化物触媒材料と、窒素酸化物を含
む排気ガスを接触させることを特徴とする窒素酸化物除
去方法。
2. In an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present, at least nickel (N
i) and gallium (Ga) as the main metal elements, a spinel-type composite oxide containing alumina (Al 2 O
A method for removing nitrogen oxides, which comprises contacting an exhaust gas containing nitrogen oxides with an oxide catalyst material formed by mixing 3 ).
JP29425594A 1994-11-29 1994-11-29 Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides Expired - Fee Related JP3309024B2 (en)

Priority Applications (1)

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Application Number Priority Date Filing Date Title
JP29425594A JP3309024B2 (en) 1994-11-29 1994-11-29 Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides

Publications (2)

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JPH08150337A true JPH08150337A (en) 1996-06-11
JP3309024B2 JP3309024B2 (en) 2002-07-29

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Country Link
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