JPH0824650A - 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

Info

Publication number
JPH0824650A
JPH0824650A JP6170631A JP17063194A JPH0824650A JP H0824650 A JPH0824650 A JP H0824650A JP 6170631 A JP6170631 A JP 6170631A JP 17063194 A JP17063194 A JP 17063194A JP H0824650 A JPH0824650 A JP H0824650A
Authority
JP
Japan
Prior art keywords
oxide
nitrogen oxides
exhaust gas
catalyst material
nox
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
JP6170631A
Other languages
Japanese (ja)
Other versions
JP3346653B2 (en
Inventor
Yoshihiro Yuu
喜裕 由宇
Masanobu Ishida
政信 石田
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
Application filed by Kyocera Corp filed Critical Kyocera Corp
Priority to JP17063194A priority Critical patent/JP3346653B2/en
Publication of JPH0824650A publication Critical patent/JPH0824650A/en
Application granted granted Critical
Publication of JP3346653B2 publication Critical patent/JP3346653B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F02COMBUSTION ENGINES; HOT-GAS OR COMBUSTION-PRODUCT ENGINE PLANTS
    • F02BINTERNAL-COMBUSTION PISTON ENGINES; COMBUSTION ENGINES IN GENERAL
    • F02B3/00Engines characterised by air compression and subsequent fuel addition
    • F02B3/06Engines characterised by air compression and subsequent fuel addition with compression ignition

Landscapes

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

Abstract

PURPOSE:To provide an oxide catalyst material having a NOx reduction- decomposition function even in an atmosphere of a high oxygen concentration and to purify exhaust gas from combustion engines such as diesel engines and lean-burn engines. CONSTITUTION:A material in which 5-75wt.% of CeO2 is incorporated into a spinel type crystalline complex oxide containing metal elements of Ni and Ga as an oxide catalyst material which reduces and decomposes nitrogen oxides such as NOx and in which a Ga/Ni atomic ratio (n) is 2.5 3.3 is used come into contact with exhaust gas containing nitrogen oxides in an oxidative atmosphere in which oxygen of a high concentration and carbon-containing gas which has a reducing function exist so as to reduce, to decompose, and to remove 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、新規な窒素酸化物を還
元除去することのできる酸化物触媒材料およびこれを用
いて排ガス中の窒素酸化物を除去する方法に関する。
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 oxide catalyst material.

【0002】[0002]

【従来技術】近年、環境汚染が問題となり、その中でも
自動車の排ガス中に含まれる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。そ
こで、従来より用いられている自動車排ガスの浄化方法
としては、一酸化炭素(CO)および炭化水素(CxH
y)の酸化と、窒素酸化物(NOx)の還元を同時に行
う三元触媒が汎用されている。このような三元触媒とし
ては、Pd、Pt、Rh等の貴金属をγ−アルミナによ
りコート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る。
2. Description of the Related Art In recent years, environmental pollution has become a problem, and among them, there is an urgent need to develop a method for decomposing and removing harmful substances such as NOx and COx contained in exhaust gas of automobiles. Therefore, as a conventionally used method for purifying automobile exhaust gas, carbon monoxide (CO) and hydrocarbon (CxH
A three-way catalyst that simultaneously performs the oxidation of y) and the reduction of nitrogen oxides (NOx) is widely used. As such a three-way catalyst, one having a noble metal such as Pd, Pt, or Rh supported on a refractory carrier such as cordierite coated with γ-alumina is used.

【0003】[0003]

【発明が解決しようとする問題点】しかし、上記三元触
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%以上の高濃度雰囲気では有効に働かなくな
るという問題点がある。そこで、通常は排気ガス中の酸
素濃度を測定して常に最適な空燃比となるように制御す
ることが行われており、これより高い酸素濃度の排気ガ
ス浄化はほとんどできていないのが現状である。
However, the above 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%. There is a problem that it cannot work effectively in the above high concentration atmosphere. Therefore, it is usually practiced to measure the oxygen concentration in the exhaust gas and control it so that the air-fuel ratio will always be the optimum value. is there.

【0004】これらの問題点を解決するために高濃度酸
素共存下でもNOxを効率よく除去できる触媒の開発が
行われ、現在、高濃度酸素共存下でもNOxを除去でき
る触媒としては銅イオン交換ゼオライト、メタルシリケ
ート、アルミナ触媒が提案されている。
In order to solve these problems, a catalyst capable of efficiently removing NOx even in the presence of high-concentration oxygen has been developed, and as a catalyst capable of removing NOx even in the presence of high-concentration oxygen, copper ion-exchanged zeolite is currently used. , Metal silicate and alumina catalysts have been proposed.

【0005】また、本発明者らは、先に、酸素を過剰に
含むとともに窒素酸化物を含む排ガスをニッケルガレー
ト(NiGa2 4 )スピネル型複合酸化物触媒と接触
させて排気ガス中の窒素酸化物を除去する方法を提案し
た。
Further, the inventors of the present invention previously contacted the exhaust gas containing excess oxygen and nitrogen oxides with a nickel gallate (NiGa 2 O 4 ) spinel type composite oxide catalyst to obtain nitrogen in exhaust gas. A method of removing oxide was proposed.

【0006】しかしながら、上記提案した触媒はNOx
除去活性温度範囲が狭く、例えば、ニッケルガレートス
ピネル型複合酸化物触媒のNOx除去率30%以上を示
す温度範囲は370〜480℃の温度域であり、特定さ
れた温度範囲しかNOxが除去されないという問題があ
った。また、上記触媒は反応ガス中に水蒸気が存在する
と特性が著しく低下し、例えば、反応ガス中に水蒸気が
10%共存するとNOx除去率は81%から25%まで
低下し、上記触媒の実用化を困難にしていた。
However, the catalyst proposed above is NOx.
The removal activity temperature range is narrow, and for example, the temperature range in which the NOx removal rate of the nickel gallate spinel type composite oxide catalyst is 30% or more is the temperature range of 370 to 480 ° C, and NOx is removed only in the specified temperature range. There was a problem. Further, the characteristics of the above catalyst are remarkably deteriorated when water vapor is present in the reaction gas. For example, when 10% of water vapor coexists in the reaction gas, the NOx removal rate is reduced from 81% to 25%. It was difficult.

【0007】[0007]

【問題点を解決するための手段】本発明者らは、上記の
問題点に対して研究を進めた結果、金属元素としてNi
とGaを含みGa/Ni原子比nが2.5〜3.3の比
率からなるスピネル型結晶性複合酸化物にCeO2 を5
〜75重量%添加した触媒材料が高酸素濃度雰囲気下で
も高いNOx除去率でしかも広い温度範囲で触媒作用を
有し、さらに共存水蒸気による性能低下が少ないことを
見いだした。
[Means for Solving the Problems] The inventors of the present invention have conducted research on the above problems, and as a result, as a metal element, Ni
CeO 2 is added to a spinel-type crystalline composite oxide containing Ga and Ni and having a Ga / Ni atomic ratio n of 2.5 to 3.3.
It was found that the catalyst material added by up to 75% by weight has a high NOx removal rate even in a high oxygen concentration atmosphere, has a catalytic action in a wide temperature range, and has little performance deterioration due to coexisting steam.

【0008】さらに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前記酸化物触媒材料と窒素酸
化物を含む排ガスと接触させることによりNOx分解除
去を効率的に行うことができることを見出したのであ
る。
Further, it was found that NOx decomposition and removal can be efficiently performed by contacting the oxide catalyst material with the exhaust gas containing nitrogen oxide in an oxidizing atmosphere in which a carbon-containing gas having a reducing property with oxygen is present. It was.

【0009】以下、本発明を詳述する。本発明において
用いられる複合酸化物はニッケル(Ni)およびガリウ
ム(Ga)を金属元素として含み、Ga/Ni原子比n
が2.5〜3.3の比率からなるスピネル型複合酸化物
である。これを一般式で表現するとNiGan O4+δ
(n=2.5〜3.3)と表される。なお、式中の(O
4+δ)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、nの値によって随時変化するものであり
0〜2.0の範囲で変化する。本発明で用いられる複合
酸化物はGa/Ni原子比nの値が2.8〜3.1が好
ましい。このうち、n=3.0のものが特に好ましい。
n値を上記の範囲に限定したのは、n値がこの範囲を逸
脱すると触媒としての活性が低下するためである。
The present invention will be described in detail below. The composite oxide used in the present invention contains nickel (Ni) and gallium (Ga) as metal elements and has a Ga / Ni atomic ratio n.
Is a spinel-type composite oxide having a ratio of 2.5 to 3.3. If this is expressed by a general formula, NiGanO 4+ δ
(N = 2.5 to 3.3). In addition, (O in the formula
4+ δ) is the amount of oxygen necessary for stable existence as a complex oxide, which changes as needed depending on the value of n, and changes in the range of 0 to 2.0. The complex oxide used in the present invention preferably has a Ga / Ni atomic ratio n of 2.8 to 3.1. Of these, n = 3.0 is particularly preferable.
The reason for limiting the n value to the above range is that if the n value deviates from this range, the activity as a catalyst decreases.

【0010】本発明によれば、この複合酸化物にCeO
2 を全量に対する比率が5〜75重量%、特に20〜4
0重量%となる量で添加する。CeO2 の添加量が75
重量%を超えると触媒活性が低下し、5重量%より少な
いと高い除去率を有する温度範囲が狭くなるためであ
る。
According to the present invention, CeO is added to this composite oxide.
The ratio of 2 to the total amount is 5 to 75% by weight, especially 20 to 4
It is added in an amount of 0% by weight. The amount of CeO 2 added is 75
This is because if the amount exceeds 5% by weight, the catalytic activity decreases, and if it is less than 5% by weight, the temperature range having a high removal rate becomes narrow.

【0011】本発明によれば上記CeO2 を添加した複
合酸化物を窒素酸化物(NOx )を含有する排ガスと接
触させることにより排ガス中に含まれる酸素濃度が1%
以上、特に3%以上の高濃度であっても広い温度範囲で
優れたNOx還元分解能を有する。さらに、雰囲気中に
2 4 、C3 6 、C3 8 等の炭化水素、CH3
H、C2 5 OH等のアルコール、CO等の還元性を有
する炭素含有ガスを含有させて前記触媒材料と接触させ
ると、NOx 還元性はさらに高くなる。
According to the present invention, the oxygen concentration in the exhaust gas is reduced to 1% by bringing the above-mentioned CeO 2 -added composite oxide into contact with the exhaust gas containing nitrogen oxide (NOx).
As described above, it has excellent NOx reduction resolution over a wide temperature range even at a high concentration of 3% or more. Further, in the atmosphere, hydrocarbons such as C 2 H 4 , C 3 H 6 , C 3 H 8 and CH 3 O
The NOx reducibility is further enhanced by incorporating an alcohol such as H, C 2 H 5 OH, etc., and a carbon-containing gas having a reducibility such as CO into contact with the catalyst material.

【0012】本発明の酸化物材料を製造するには、例え
ば、NiやGaの酸化物や熱処理により酸化物を生成で
きるこれらの金属の炭酸塩、硝酸塩、酢酸塩等を用い
る。これらをGa/Niの原子比が2.5〜3.3にな
るように秤量混合した後、これを500〜1600℃の
酸化性雰囲気中で5〜30時間熱処理することによりN
iおよびGaのスピネル型結晶を主結晶相とする複合酸
化物粉末を得ることができる。
To produce the oxide material of the present invention, for example, oxides of Ni and Ga, and carbonates, nitrates, acetates and the like of these metals capable of forming oxides by heat treatment are used. These are weighed and mixed so that the Ga / Ni atomic ratio is 2.5 to 3.3, and then heat treated for 5 to 30 hours in an oxidizing atmosphere at 500 to 1600 ° C. to obtain N.
It is possible to obtain a complex oxide powder having a spinel type crystal of i and Ga as a main crystal phase.

【0013】また、その他の方法として酸化物や他の金
属塩による固相反応合成、金属アルコキシドを用いたゾ
ル−ゲル法合成によっても製造することができる。いず
れも熱処理は500〜1600℃の酸化性雰囲気中で5
〜30時間行われ、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る。しかし、熱処
理温度が500℃より低いと結晶化が不十分となり、1
600℃を越えると緻密化してしまうため好ましくな
い。好適な熱処理温度は650〜750℃である。
As other methods, solid phase reaction synthesis with oxides and other metal salts, and sol-gel method synthesis using metal alkoxide can also be used for production. In each case, the heat treatment is performed in an oxidizing atmosphere at 500 to 1600 ° C.
It is effective to perform the heat treatment at a low temperature for about 30 hours to increase the specific surface area of the powder. However, if the heat treatment temperature is lower than 500 ° C, crystallization becomes insufficient and
If the temperature exceeds 600 ° C., the composition is densified, which is not preferable. A suitable heat treatment temperature is 650 to 750 ° C.

【0014】さらに、CeO2 の添加方法としては、C
eO2 粉末と上記複合酸化物粉末をボールミル粉砕混合
または乳鉢内で粉砕混合する方法があるが、本発明は、
これに限定されるものではない。なお、この時の複合酸
化物粉末の比表面積は30〜100m2 /g、特に40
〜80m2 /gであることが好ましく、CeO2 粉末の
比表面積は10〜100m2 /g、特に15〜60m2
/gであることが好ましい。
Further, as a method of adding CeO 2 , C
There is a method of pulverizing and mixing the eO 2 powder and the above complex oxide powder with a ball mill or in a mortar.
It is not limited to this. The specific surface area of the composite oxide powder at this time is 30 to 100 m 2 / g, and especially 40
Preferably ~80m is 2 / g, the specific surface area of CeO 2 powder 10 to 100 m 2 / g, especially 15 to 60 2
/ G is preferable.

【0015】[0015]

【作用】本発明によれば、金属元素としてNiとGaを
含みGa/Ni原子比nが2.5〜3.3の比率からな
るスピネル型結晶性複合酸化物にCeO2 を5〜75重
量%添加した触媒材料を窒素酸化物を含む排気ガスと接
触させることによりNOxを高効率で、しかも広い温度
範囲で還元除去することができ、共存水蒸気による性能
低下が少ない。
According to the present invention, 5 to 75 weight% of CeO 2 is added to a spinel type crystalline composite oxide containing Ni and Ga as metal elements and having a Ga / Ni atomic ratio n of 2.5 to 3.3. % Of NOx can be reduced and removed with high efficiency by contacting the exhaust gas containing nitrogen oxides with exhaust gas, and the performance deterioration due to coexisting steam is small.

【0016】この還元分解はNOよりもNO2 の方が反
応性がよく、CeO2 およびNiGa2 4 単独のNO
x還元分解特性よりも本発明の材料の方が300〜55
0℃の広い温度域で高いNOx還元分解特性を得ている
ことから、上記複合酸化物にCeO2 を添加することに
よりNOをNO2 に酸化する性能が向上し触媒特性が向
上したと考えられる。
This reductive decomposition is more reactive with NO 2 than with NO, and NO of CeO 2 and NiGa 2 O 4 alone is used.
x The material of the present invention is 300 to 55 than the reductive decomposition property.
Since high NOx reduction decomposition characteristics were obtained in a wide temperature range of 0 ° C, it is considered that the addition of CeO 2 to the above composite oxide improved the ability to oxidize NO into NO 2 and improved the catalyst characteristics. .

【0017】[0017]

【実施例】出発原料としてNi(NO3 2 ・6H
2 O、Ga(NO3 2 ・9H2 Oを用い、Ni:Ga
の金属比が表1の比率になるように秤量した。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
で中和した。生じた沈殿物を濾過、洗浄し、凍結乾燥さ
せた。乾燥した粉末を700℃で30時間、大気中で熱
処理し比表面積40〜50m2 /gのスピネル型結晶性
複合酸化物粉末を得た。
EXAMPLES Ni (NO 3) as the starting material 2 · 6H
2 O, Ga (NO 3) using a 2 · 9H 2 O, Ni: Ga
Were weighed so that the metal ratio of was the ratio shown in Table 1. These reagents were dissolved in distilled water and neutralized with aqueous ammonia while stirring. The precipitate formed was filtered, washed and freeze-dried. The dried powder was heat-treated at 700 ° C. for 30 hours in the air to obtain a spinel type crystalline complex oxide powder having a specific surface area of 40 to 50 m 2 / g.

【0018】さらに、この複合酸化物粉末に対し表1に
示す量の比表面積15m2 /gのCeO2 粉末を混合し
た。次に、混合した粉末を金型プレスにより成形後、冷
間静水圧成形法によりさらに圧縮成形し、その成形物を
解砕し25メッシュパス、35メッシュオンの粉末に整
粒した。ついで、この粉末を用いて、排ガスとしてNO
=1000ppm、O2 =5%、C2 4 =1000p
pm、He=残部のガス、SV(空間速度)=4000
0/hの条件で、300〜600℃の範囲でNO還元分
解能およびエチレンの分解能をガスクロマトグラフを用
いて測定した。それぞれの試料のNO最高活性とNO除
去率30%以上を示す温度範囲と上記排ガス中に水蒸気
が10%含まれるガスでNO還元分解能を測定した結果
を表1に示す。
Further, CeO 2 powder having a specific surface area of 15 m 2 / g in an amount shown in Table 1 was mixed with this composite oxide powder. Next, the mixed powder was molded by a die press and further compression-molded by a cold isostatic pressing method, and the molded product was crushed and sized to powder of 25 mesh pass, 35 mesh on. Then, using this powder, NO as exhaust gas
= 1000 ppm, O 2 = 5%, C 2 H 4 = 1000 p
pm, He = balance gas, SV (space velocity) = 4000
Under the condition of 0 / h, the NO reduction resolution and the ethylene resolution were measured in the range of 300 to 600 ° C. using a gas chromatograph. Table 1 shows the results of measuring the NO reduction resolution in the temperature range in which the maximum NO activity and the NO removal rate of 30% or more of each sample and the gas in which the exhaust gas contains 10% of water vapor.

【0019】[0019]

【表1】 [Table 1]

【0020】表1から明らかなようにGa/Ni比が
3.0の複合酸化物にCeO2 を5重量%添加しただけ
でNOx除去率が30%以上を示す温度範囲が50℃広
くなった。さらにCeO2 を35重量%添加するとさら
に40℃広くなった。しかし、90重量%を超えて添加
すると最高活性値が低下することや、nの値が2.5〜
3.3の範囲で最高活性値が高く、NOx除去率30%
以上を示す温度範囲も広いことがわかった。
As is apparent from Table 1, the addition of 5% by weight of CeO 2 to the composite oxide having a Ga / Ni ratio of 3.0 widens the temperature range in which the NOx removal rate is 30% or more by 50 ° C. . When CeO 2 was added in an amount of 35% by weight, the temperature was further increased by 40 ° C. However, when the amount added exceeds 90% by weight, the maximum activity value decreases and the value of n is 2.5 to
Highest activity value in the range of 3.3, NOx removal rate 30%
It was found that the temperature range showing the above is wide.

【0021】また、表1から明らかなようにGa/Ni
比が3.0の複合酸化物単独の水蒸気共存下でのNOx
除去率は81%から25%まで低下した。しかし、Ga
/Ni比が3.0の複合酸化物にCeO2 を5重量%添
加しただけで水蒸気共存下でのNOx除去率が25%か
ら40%に向上した。さらにCeO2 を35重量%添加
すると65%まで向上した。しかし、90重量%を超え
て添加するとNOx除去率は20%まで低下することが
わかった。
As is clear from Table 1, Ga / Ni
NOx in the coexistence of steam with a complex oxide having a ratio of 3.0 alone
The removal rate decreased from 81% to 25%. However, Ga
The NOx removal rate in the presence of water vapor was improved from 25% to 40% simply by adding 5% by weight of CeO 2 to the composite oxide having a / Ni ratio of 3.0. Further, when CeO 2 was added in an amount of 35% by weight, the content improved to 65%. However, it was found that the NOx removal rate decreases to 20% when added in excess of 90% by weight.

【0022】[0022]

【発明の効果】以上、詳述した通り、本発明による触媒
材料は高酸素濃度雰囲気下でも広温度範囲で高いNOx
還元分解作用を有し、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燃焼機関の排気ガス等の浄化に有
用なものである。
As described above in detail, the catalyst material according to the present invention has high NOx in a wide temperature range even in a high oxygen concentration atmosphere.
It has a reducing decomposition action and is useful for purification of exhaust gas from combustion engines such as diesel engines and lean burn engines in the future.

───────────────────────────────────────────────────── 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 A 102 G ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location B01D 53/36 102 A A 102 G

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】金属元素としてNiとGaを含みGa/N
i原子比nが2.5〜3.3の比率からなるスピネル型
結晶性複合酸化物にCeO2 を5〜75重量%添加して
なる窒素酸化物除去用酸化物触媒材料。
1. A Ga / N containing Ni and Ga as metal elements.
An oxide catalyst material for removing nitrogen oxides, which is obtained by adding 5 to 75% by weight of CeO 2 to a spinel type crystalline complex oxide having an i atomic ratio n of 2.5 to 3.3.
【請求項2】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、金属元素としてNiとGaを含み
Ga/Ni原子比nが2.5〜3.3の比率からなるス
ピネル型結晶性複合酸化物にCeO2 を5〜75重量%
添加してなる窒素酸化物除去用酸化物触媒材料を窒素酸
化物を含む排ガスと接触させることを特徴とする窒素酸
化物除去方法。
2. A spinel type which contains Ni and Ga as metal elements and has a Ga / Ni atomic ratio n of 2.5 to 3.3 in an oxidizing atmosphere in which a carbon-containing gas having a reducing property with oxygen is present. 5 to 75% by weight of CeO 2 in the crystalline composite oxide
A method for removing nitrogen oxides, which comprises contacting the added oxide catalyst material for removing nitrogen oxides with an exhaust gas containing nitrogen oxides.
JP17063194A 1994-07-22 1994-07-22 Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides Expired - Fee Related JP3346653B2 (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH039719A (en) * 1989-02-16 1991-01-17 Matsushita Electric Ind Co Ltd Automatic cleaner

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH039719A (en) * 1989-02-16 1991-01-17 Matsushita Electric Ind Co Ltd Automatic cleaner

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