JPH0838902A - Exhaust gas purification catalyst and device - Google Patents
Exhaust gas purification catalyst and deviceInfo
- Publication number
- JPH0838902A JPH0838902A JP6175118A JP17511894A JPH0838902A JP H0838902 A JPH0838902 A JP H0838902A JP 6175118 A JP6175118 A JP 6175118A JP 17511894 A JP17511894 A JP 17511894A JP H0838902 A JPH0838902 A JP H0838902A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- exhaust gas
- nitrogen oxides
- internal combustion
- oxide
- 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
Links
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F02—COMBUSTION ENGINES; HOT-GAS OR COMBUSTION-PRODUCT ENGINE PLANTS
- F02B—INTERNAL-COMBUSTION PISTON ENGINES; COMBUSTION ENGINES IN GENERAL
- F02B3/00—Engines characterised by air compression and subsequent fuel addition
- F02B3/06—Engines characterised by air compression and subsequent fuel addition with compression ignition
Landscapes
- Exhaust Gas After Treatment (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Abstract
(57)【要約】
【目的】窒素酸化物を高効率に浄化するための排気ガス
浄化方法を提供する。
【構成】Ni,Feを含むスピネル型酸化物であること
を特徴とする排気ガス浄化触媒を用いて内燃機関の酸素
を含む排気ガスから窒素酸化物を除去する。
【効果】本発明によれば、酸素過剰雰囲気下での排ガス
から、窒素酸化物を効率的に浄化することができる。
(57) [Summary] [Objective] To provide an exhaust gas purification method for purifying nitrogen oxides with high efficiency. A nitrogen oxide is removed from an exhaust gas containing oxygen of an internal combustion engine by using an exhaust gas purifying catalyst which is a spinel type oxide containing Ni and Fe. [Effect] According to the present invention, nitrogen oxides can be efficiently purified from exhaust gas in an oxygen excess atmosphere.
Description
【0001】[0001]
【産業上の利用分野】本発明は、酸素を含む燃焼排ガス
の浄化触媒及び装置であって、特に窒素酸化物を浄化す
る触媒及び装置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a catalyst and a device for purifying combustion exhaust gas containing oxygen, and more particularly to a catalyst and a device for purifying nitrogen oxides.
【0002】[0002]
【従来の技術】自動車等の内燃機関から排出される排気
ガスには、窒素酸化物等が含まれ、それらは人体に有害
であるに加え酸性雨など地球環境破壊の原因となる。そ
こで、排気ガス中の窒素酸化物を浄化する方法について
種々検討がなされている。2. Description of the Related Art Exhaust gas emitted from an internal combustion engine of an automobile or the like contains nitrogen oxides and the like, which are harmful to humans and also cause environmental damage such as acid rain. Therefore, various studies have been made on methods for purifying nitrogen oxides in exhaust gas.
【0003】現在、自動車においてはエンジンの空燃比
はストイキつまり理論空燃比(A/F=14.6:空気
Aと燃料Fの重量比)付近に設定され、生成する排ガス
は貴金属(ロジウム,パラジウム,白金)を主体とした
三元触媒で窒素酸化物を窒素に還元,炭化水素,一酸化
炭素は酸化することにより浄化している。At present, in automobiles, the air-fuel ratio of the engine is set to a stoichiometric value, that is, near the stoichiometric air-fuel ratio (A / F = 14.6: weight ratio of air A to fuel F), and the exhaust gas produced is made of precious metals (rhodium, palladium). , Platinum) is used as a three-way catalyst to reduce nitrogen oxides to nitrogen, and hydrocarbons and carbon monoxide are oxidized to purify them.
【0004】ところで、自動車については、近年、燃料
消費率低減の観点から、空燃比を理論空燃比(14.6)
以上とする希薄燃焼(リーンバーン)エンジンの開発が
進められ、その普及が期待されている。しかし、リーン
バーンエンジンでは、理論空燃比に比べ排気ガス中に酸
素が過剰に(少なくとも0.5%以上)含まれるため、現
用の三元触媒では炭化水素と一酸化炭素の酸化のみが進
行し、窒素酸化物の還元を効果的に行うことができな
い。By the way, regarding automobiles, in recent years, from the viewpoint of reducing the fuel consumption rate, the air-fuel ratio is changed to the theoretical air-fuel ratio (14.6).
Development of the lean burn engine described above has been promoted and its spread is expected. However, in a lean burn engine, oxygen is contained in the exhaust gas in excess (at least 0.5% or more) compared to the stoichiometric air-fuel ratio, so in the currently used three-way catalyst, only oxidation of hydrocarbons and carbon monoxide proceeds. However, reduction of nitrogen oxides cannot be performed effectively.
【0005】一方、ディーゼル自動車等のディーゼルエ
ンジンは従来より酸素過剰の高空燃比で運転されてい
る。従って、上記三元触媒の適用が出来ず、有効な窒素
酸化物の低減法を見出せないでいる。On the other hand, diesel engines such as diesel automobiles are conventionally operated at a high air-fuel ratio with excess oxygen. Therefore, the above three-way catalyst cannot be applied, and an effective method for reducing nitrogen oxides cannot be found.
【0006】現在実用化されている窒素酸化物の除去方
法の一つに、V2O3−TiO2 触媒を用いたNH3 還元
法がある。この方法は、排ガス中に多量の酸素が共存し
ても窒素酸化物を除去できることが特徴である。しかし
ながらこの方法は、有害物質であるNH3 を使用するこ
と、及びNH3 供給タンクを必要とするため自動車等の
移動式小型内燃機関には利用されにくい。One of the methods for removing nitrogen oxides currently in practical use is the NH 3 reduction method using a V 2 O 3 —TiO 2 catalyst. This method is characterized in that nitrogen oxides can be removed even if a large amount of oxygen coexists in the exhaust gas. However, this method uses NH 3 , which is a harmful substance, and requires an NH 3 supply tank, and thus is difficult to be used for a mobile small internal combustion engine such as an automobile.
【0007】そこで、近年、酸素過剰共存下の酸化雰囲
気において、NH3 を使わずに窒素酸化物を浄化する触
媒の研究が盛んに行われている。その中でも、排気ガス
中に含まれる炭化水素と酸素を利用して窒素酸化物を除
去する方法が注目されている。Therefore, in recent years, much research has been conducted on a catalyst for purifying nitrogen oxides without using NH 3 in an oxidizing atmosphere in the presence of excess oxygen. Among them, a method of removing nitrogen oxides by utilizing hydrocarbon and oxygen contained in the exhaust gas has attracted attention.
【0008】現在、そのような触媒として、ゼオライト
に銅を担持した触媒(特開平4−219141号公報,第69
回触媒討論会予行集3F108(1992))やゼオライ
トにコバルト,希土類,銅およびまたはロジウムを含む
触媒(特開平4−219147 号公報)が報告されている。Currently, as such a catalyst, a catalyst in which copper is supported on zeolite (Japanese Patent Laid-Open No. 4-219141, No. 69)
The 3rd Demonstration Meeting on the 3rd Debriefing of the 3rd catalyst 108 (1992)) and a catalyst containing cobalt, rare earth, copper and / or rhodium in zeolite (JP-A-4-219147) have been reported.
【0009】[0009]
【発明が解決しようとする課題】しかし前述の方法にお
いては、ゼオライトに銅を担持した触媒(特開平1−151
706号公報)は、銅の窒素酸化物に対する特異な吸着特
性から低温度域において極めて高い性能を示すが、触媒
作用を示す温度域(ウインドウ)が狭い。However, in the above-mentioned method, a catalyst in which copper is supported on zeolite (JP-A-1-151
No. 706) shows extremely high performance in a low temperature range due to the unique adsorption property of copper to nitrogen oxides, but the temperature range (window) in which a catalytic action is exhibited is narrow.
【0010】そこで、ウインドウを広げることを目的と
した触媒,ゼオライトにコバルト,希土類,銅,ロジウ
ムを含む触媒(特開平4−219147 号公報)が提案され、
比較的広い温度域で窒素酸化物を浄化することができる
ようになった。また、ゼオライトに銅を担持した触媒
(第69回触媒討論会予行集3F108(1992))は
多量の水が共存すると触媒活性が低下することが知られ
ている。しかしながら、担体であるゼオライトの水熱耐
久性は700℃が限界とも言われており、80℃の耐久
性が要求される自動車用触媒としては更に高い窒素酸化
物浄化性能と耐久性が要求されている。Therefore, a catalyst for expanding the window, a catalyst containing cobalt, rare earth, copper, and rhodium in zeolite (Japanese Patent Laid-Open No. 4-219147) is proposed,
It has become possible to purify nitrogen oxides in a relatively wide temperature range. In addition, it is known that the catalyst in which copper is supported on zeolite (The 69th Catalytic Discussion Group, Proceedings 3F108 (1992)) has a decreased catalytic activity when a large amount of water coexists. However, the hydrothermal durability of zeolite as a carrier is said to be limited to 700 ° C, and further higher nitrogen oxide purification performance and durability are required for automobile catalysts that require durability of 80 ° C. There is.
【0011】[0011]
【課題を解決するための手段】上記を解決するためにな
されたものであって、本発明者は作用温度域が広く、蒸
気の影響が小さく、かつ反応前後で触媒構造が変化しに
くい触媒について鋭意検討した結果、NiおよびFeの
少なくとも一つを含み、特に化学式AB2O4で記述され
るスピネル型酸化物触媒は本目的にかなうことを見出し
た。In order to solve the above-mentioned problems, the present inventor has proposed a catalyst having a wide operating temperature range, a small effect of steam, and a catalyst structure which is difficult to change before and after the reaction. As a result of earnest studies, it was found that a spinel type oxide catalyst containing at least one of Ni and Fe and particularly described by the chemical formula AB 2 O 4 can serve this purpose.
【0012】本発明は、Ni及びFeの少なくとも一つ
を含むスピネル型複合酸化物であることを特徴とする。
または、Ni及びFeの少なくとも一つを含み、化学式
AB2O4(A,Bは金属元素)で記述される酸化物であ
ることを特徴とする。The present invention is characterized by being a spinel type composite oxide containing at least one of Ni and Fe.
Alternatively, it is an oxide containing at least one of Ni and Fe and described by the chemical formula AB 2 O 4 (A and B are metal elements).
【0013】前記触媒の少なくとも一つを用いて内燃機
関の酸素を含む排気ガスから窒素酸化物を除去すること
ができる。At least one of the catalysts can be used to remove nitrogen oxides from the exhaust gas containing oxygen of an internal combustion engine.
【0014】上記触媒調製に用いる金属塩は、硝酸塩,
酢酸塩,塩酸塩,硫酸塩,炭酸塩などがあり、本発明は
これらの金属塩の種類に限定されるもではない。The metal salt used for the above catalyst preparation is nitrate,
There are acetates, hydrochlorides, sulfates, carbonates, etc., and the present invention is not limited to these kinds of metal salts.
【0015】本発明となる触媒調製方法として、それぞ
れの金属塩を一旦酸化物にした後に混合焼成する方法ま
たは金属塩を混合し焼成する方法などあるが任意であ
る。The catalyst preparation method of the present invention includes any method, such as a method of once converting each metal salt into an oxide and then mixing and firing the mixture, or a method of mixing and firing the metal salts.
【0016】金属塩を酸化物にする場合、500℃以上
750℃未満で焼成する。スピネル型酸化物を得るとき
には、900℃以上100℃未満で2時間以上10時間
未満焼成処理することが望ましい。When the metal salt is converted to an oxide, it is fired at 500 ° C. or higher and lower than 750 ° C. When obtaining a spinel-type oxide, it is desirable to perform a baking treatment at 900 ° C. or higher and lower than 100 ° C. for 2 hours or longer and shorter than 10 hours.
【0017】前記の如く製造された触媒の形状は、粉
末,粒状,ペレット状,ハニカム状など任意であり、コ
ージェライト,メタルハニカムなど任意の多孔質担体に
担持して使用することも可能である。The catalyst produced as described above may have any shape such as powder, granules, pellets, or honeycomb, and it can be used by supporting it on any porous carrier such as cordierite or metal honeycomb. .
【0018】本触媒は少なくとも酸素、一酸化炭素,炭
化水素及び窒素酸化物を含むガスに適用でき、ガソリン
エンジン排気ガス,ディーゼルエンジン排気ガス等の内
燃機関排気ガスに使用することができる。The present catalyst can be applied to gases containing at least oxygen, carbon monoxide, hydrocarbons and nitrogen oxides, and can be used for internal combustion engine exhaust gases such as gasoline engine exhaust gas and diesel engine exhaust gas.
【0019】本発明触媒の使用条件は、 触媒温度もしくは排気ガス温度:100℃以上800℃
以下、好ましくは200℃以上500℃以下 酸素濃度:0.5%以上20%以下で使用することが望
ましく、窒素酸化物濃度及び炭化水素濃度はC/N原子
比で0.5 以上10以下、好ましくは1〜5程度で使用
することが望ましい。The use conditions of the catalyst of the present invention are as follows: catalyst temperature or exhaust gas temperature: 100 ° C. or higher and 800 ° C.
Below, preferably 200 ℃ or more and 500 ℃ or less Oxygen concentration: It is desirable to use at 0.5% or more and 20% or less, nitrogen oxide concentration and hydrocarbon concentration is 0.5 or more and 10 or less in C / N atomic ratio, Preferably, it is desirable to use 1 to 5 or so.
【0020】前述の如く、本触媒によりリーンバーンエ
ンジンやディーゼルエンジン等の排ガスから窒素酸化物
を除去することが可能である。本発明によって製造され
た触媒の基本的な使用方法は、図1に示すように本触媒
を反応器内に配置し該反応器内に排気ガスを流通させ、
本触媒と排気ガスを接触させて窒素酸化物を浄化し、排
気ガスを反応器外へ排出させることである。また、図2
のように本触媒は内燃機関と三元触媒との間に配置して
も良い。また、図3のように、内燃機関がストイキ条件
で運転される時には三元触媒のみに排ガスが流れる構成
(例えばバイパスを設けるなど)にしても良い。さら
に、図4に示すように、本触媒成分を三元触媒に含ませ
ても良いし、三元触媒の上に担持させて用いても良い。As described above, the present catalyst can remove nitrogen oxides from exhaust gas from lean burn engines, diesel engines, and the like. The basic method of using the catalyst produced according to the present invention is as shown in FIG. 1, in which the present catalyst is placed in a reactor and exhaust gas is circulated in the reactor.
This is to bring the catalyst and exhaust gas into contact with each other to purify nitrogen oxides and to discharge the exhaust gas out of the reactor. Also, FIG.
As described above, the present catalyst may be arranged between the internal combustion engine and the three-way catalyst. Further, as shown in FIG. 3, when the internal combustion engine is operated under stoichiometric conditions, the exhaust gas may flow only to the three-way catalyst (for example, a bypass is provided). Further, as shown in FIG. 4, the present catalyst component may be contained in the three-way catalyst, or may be supported on the three-way catalyst for use.
【0021】図5は、多孔質ハニカムに本触媒成分をコ
ートし、その上に三元触媒成分をコートする方法であ
る。コートの上下関係は逆でも良い。FIG. 5 shows a method in which a porous honeycomb is coated with the present catalyst component and then a three-way catalyst component is coated thereon. The top and bottom of the coat may be reversed.
【0022】[0022]
【作用】酸素過剰及び炭化水素共存下で窒素酸化物を浄
化する反応機構については明らかではないが、本発明に
含まれるNiFe2O4を例にとりその作用は次の様に発
現すると考えられる。Although the reaction mechanism for purifying nitrogen oxides in the presence of excess oxygen and hydrocarbons is not clear, taking NiFe 2 O 4 included in the present invention as an example, it is considered that its action is expressed as follows.
【0023】上記発明に用いるスピネル型酸化物は化学
一般式、AB2O4(A,Bは金属元素)で表わせられ、
900℃以上の高温度耐久性のある物質である。NiFe
2O4スピネル酸化物は、プロピレンの完全酸化活性にお
いてNi酸化物やFe酸化物より活性が低いとされてい
る。NOxの浄化反応は炭化水素とNOxと酸素が反応
物質であることから、炭化水素の燃焼のみが進行すると
NOx浄化性能が悪くなる。従って、NiFe2O4はス
ピネル構造をとることで炭化水素燃焼活性を弱めてNO
x浄化性能を保っていると考えられる。The spinel type oxide used in the above invention is represented by the general chemical formula AB 2 O 4 (A and B are metallic elements).
It is a substance with high temperature durability of 900 ° C or higher. NiFe
The 2 O 4 spinel oxide is said to be less active than the Ni oxide and the Fe oxide in the complete oxidation activity of propylene. Since hydrocarbons, NOx, and oxygen are reaction substances in the NOx purification reaction, the NOx purification performance deteriorates when only the combustion of hydrocarbons progresses. Therefore, NiFe 2 O 4 has a spinel structure to weaken the hydrocarbon combustion activity and NO
x It is considered that the purification performance is maintained.
【0024】上記の作用によってNi,Feを含むスピ
ネル型触媒は耐久性に優れ、かつ窒素酸化物を効率良く
除去することが可能であると思われる。By the above action, it is considered that the spinel type catalyst containing Ni and Fe has excellent durability and can remove nitrogen oxides efficiently.
【0025】[0025]
【実施例】以下、実施例によって本発明を具体的に説明
するが、本発明はこれらの実施例によって制限されるも
のではない。The present invention will be described in detail below with reference to examples, but the present invention is not limited to these examples.
【0026】(実施例1)原子比で、Ni:Fe=1:
2が得られるように触媒を調製した。実施例触媒1の場
合、金属塩として硝酸塩を用い、それぞれを上記原子比
を達成できるように加え、これに蒸留水を加え、乾燥混
合物がペースト状に変わるまでらいかい機で約15分間
混練した。前記ペーストを約100℃で約2時間乾燥
後、約900℃で10時間焼成した。続いて、室温まで
自然冷却する。この粉末触媒を粒径1mm以上2mm未満に
加圧成型して供試触媒を得た。(Example 1) In atomic ratio, Ni: Fe = 1:
The catalyst was prepared so that 2 was obtained. In the case of the catalyst of Example 1, nitrate was used as a metal salt, and each was added so that the above atomic ratio could be achieved. Distilled water was added to this, and the mixture was kneaded for about 15 minutes with a fryer until the dry mixture changed into a paste. . The paste was dried at about 100 ° C. for about 2 hours and then baked at about 900 ° C. for 10 hours. Then, it is naturally cooled to room temperature. This powder catalyst was pressure-molded to a particle size of 1 mm or more and less than 2 mm to obtain a test catalyst.
【0027】「比較例1」原子比で、Y:Sr:Co=
1/3:2/3:1になるように、実施例1に従って比
較例触媒1を調製した。"Comparative Example 1" In atomic ratio, Y: Sr: Co =
Comparative catalyst 1 was prepared according to Example 1 so that it was 1/3: 2/3: 1.
【0028】上記実施例触媒1及び比較例触媒1を次の
条件で窒素酸化物の浄化性能試験を行った。触媒3cm3
を、パイレックス製反応管に充填した。これを、電気炉
により外から加熱し、150℃にした後、反応ガスを流
通させ、10℃/mの速度で600℃まで昇温させ、反
応を行わせた。反応ガスは、リーンモデル排ガスとし
て、NO:0.06%,C3H6:0.04%,CO:0.
1%,CO2:10%,O2 :4%,水蒸気10%,残
部窒素とし、ストイキモデル排ガスとして、NO:0.
1%,C3H6:0.05%,CO:0.6%,O2:0.6
%,水蒸気10%,残部窒素を空間速度20,000h
-1 となる様に流通させた。以上の操作により浄化され
た窒素酸化物の濃度は、化学分光法で測定した。表1
に、触媒層入口温度200〜500℃での浄化率とその
ときの触媒層入口温度を示した。実施例触媒1は比較例
触媒1よりも全温度領域で高い浄化率を示した。ここ
で、浄化率は触媒層入口に対する出口での窒素酸化物の
除去率で次式に従って算出した。The catalyst of Example 1 and the catalyst of Comparative Example 1 were subjected to a nitrogen oxide purification performance test under the following conditions. Catalyst 3 cm 3
Was charged into a Pyrex reaction tube. This was heated from outside by an electric furnace to 150 ° C., and then a reaction gas was circulated to raise the temperature to 600 ° C. at a rate of 10 ° C./m to carry out a reaction. The reaction gas, as lean model exhaust gas, NO: 0.06%, C 3 H 6 : 0.04%, CO: 0.0.
1%, CO 2 : 10%, O 2 : 4%, water vapor 10%, balance nitrogen, NO: 0 as stoichiometric model exhaust gas.
1%, C 3 H 6: 0.05%, CO: 0.6%, O 2: 0.6
%, Steam 10%, balance nitrogen: space velocity 20,000h
It was distributed so that it would be -1 . The concentration of nitrogen oxides purified by the above operation was measured by chemical spectroscopy. Table 1
Shows the purification rate at the catalyst layer inlet temperature of 200 to 500 ° C. and the catalyst layer inlet temperature at that time. The catalyst of Example 1 showed a higher purification rate than the catalyst of Comparative Example 1 in the entire temperature range. Here, the purification rate is the removal rate of nitrogen oxides at the outlet with respect to the catalyst layer inlet, and was calculated according to the following equation.
【0029】[0029]
【数1】 [Equation 1]
【0030】[0030]
【表1】 [Table 1]
【0031】反応前後の粉末X線回折測定炭を行った結
果、実施例触媒1については構造変化はほとんど見られ
なかったが、比較例触媒1においてはY2O3とCo3O4
の生成が一部認められた。As a result of performing powder X-ray diffraction measurement before and after the reaction, almost no structural change was observed in Example catalyst 1, but in Comparative example catalyst 1, Y 2 O 3 and Co 3 O 4 were observed.
Was partially observed.
【0032】(実施例2)コージェライトハニカムに、
実施例触媒1を100g/lウオッシュコートし700
℃で2時間焼成した後、三元触媒成分を100g/lウ
オッシュコートして900℃で2時間焼成して、実施例
触媒2を作製した。(Example 2) In a cordierite honeycomb,
Example catalyst 1 was washed with 100 g / l of wash coat to 700
After calcination at 2 ° C. for 2 hours, 100 g / l washcoat of the three-way catalyst component was carried out and calcination at 900 ° C. for 2 hours to prepare Example catalyst 2.
【0033】実施例触媒2のハニカム体積は6cm3 と
し、パイレックス製反応管に充填した。それぞれを、電
気炉により外から加熱し、150℃にした後、反応ガス
を流通させ、10℃/mの速度で600℃まで昇温さ
せ、反応を行った。反応ガスは、リーンモデル排ガスと
して、NO:0.06%,C3H6:0.04%,CO:0.
1%,CO2:10%,O2:4%,水蒸気10%,残部
窒素を、ストイキモデル排ガスの場合は、NO:0.1
%,C3H6:0.05%,CO:0.6%,O2 : 0.
6%,水蒸気10%,残部窒素を3000cc/minの
流量で流通させた。以上の操作により浄化された窒素酸
化物の濃度は、化学分光法で測定した。250℃から4
00℃での効果はリーン排ガスでは窒素酸化物の平均除
去率:約45%、ストイキ排ガスでの平均除去率:約1
00%となった。The honeycomb volume of Example catalyst 2 was set to 6 cm 3 and was filled in a Pyrex reaction tube. Each was heated from the outside by an electric furnace to 150 ° C., and then a reaction gas was circulated to raise the temperature to 600 ° C. at a rate of 10 ° C./m to carry out a reaction. The reaction gas, as a lean model exhaust gas, NO: 0.06%, C 3 H 6: 0.04%, CO: 0.
1%, CO 2 : 10%, O 2 : 4%, steam 10%, balance nitrogen: NO: 0.1 in the case of stoichiometric model exhaust gas
%, C 3 H 6: 0.05 %, CO: 0.6%, O 2: 0.
6%, steam 10%, and the balance nitrogen were circulated at a flow rate of 3000 cc / min. The concentration of nitrogen oxides purified by the above operation was measured by chemical spectroscopy. 250 ° C to 4
The effect at 00 ° C is that the lean exhaust gas has an average nitrogen oxide removal rate of about 45%, and the stoichiometric exhaust gas has an average removal rate of about 1%.
It became 00%.
【0034】[0034]
【発明の効果】実施例から明らかのように、本発明によ
れば、900℃,10時間の高温熱履歴を経た材料で、
酸素過剰雰囲気下での排ガスから、窒素酸化物を効率的
に浄化することができる。As is apparent from the examples, according to the present invention, a material which has undergone a high temperature heat history of 900 ° C. for 10 hours,
Nitrogen oxides can be efficiently purified from exhaust gas in an oxygen excess atmosphere.
【0035】また、本発明により、窒素酸化物浄化能と
高耐久性を具備した触媒材料及びそれを用いた窒素酸化
物浄化装置が得られ、自動車の内燃機関や調理器具など
の民生用製品からの燃焼排気ガスや、工場や火力発電所
のボイラーなどから排出される産業燃焼排気ガスなど広
範囲の発生源からの窒素酸化物を浄化することが可能に
なる。Further, according to the present invention, a catalytic material having a nitrogen oxide purifying ability and a high durability and a nitrogen oxide purifying apparatus using the same can be obtained, which can be used for consumer products such as automobile internal combustion engines and cooking utensils. It is possible to purify nitrogen oxides from a wide range of sources such as the combustion exhaust gas of, and industrial combustion exhaust gas emitted from boilers of factories and thermal power plants.
【図1】スピネル型酸化物触媒による装置。FIG. 1 is an apparatus using a spinel type oxide catalyst.
【図2】スピネル型酸化物触媒と三元触媒による2段式
装置。FIG. 2 is a two-stage device using a spinel type oxide catalyst and a three-way catalyst.
【図3】バイパスを用いたスピネル型酸化物触媒と三元
触媒による装置。FIG. 3 is an apparatus using a spinel-type oxide catalyst using a bypass and a three-way catalyst.
【図4】スピネル型酸化物触媒と三元触媒による複合式
装置。FIG. 4 is a composite device using a spinel type oxide catalyst and a three-way catalyst.
【図5】多孔質ハニカム含有例。FIG. 5 shows an example of containing a porous honeycomb.
1…スピネル型酸化物触媒、2…三元触媒、3…バイパ
ス切り替えバルブ、4…バイパス流路、5…多孔質ハニ
カム。DESCRIPTION OF SYMBOLS 1 ... Spinel type oxide catalyst, 2 ... Three-way catalyst, 3 ... Bypass switching valve, 4 ... Bypass channel, 5 ... Porous honeycomb.
───────────────────────────────────────────────────── 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 F01N 3/28 301 B (72)発明者 能登 康雄 茨城県勝田市大字高場2520番地 株式会社 日立製作所自動車機器事業部内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification number Reference number within the agency FI Technical display location F01N 3/28 301 B (72) Inventor Yasuo Noto 2520 Takaba, Katsuta-shi, Ibaraki Hitachi Ltd. Factory Automotive Equipment Division
Claims (3)
ネル型複合酸化物であることを特徴とする内燃機関の酸
素を含む排気ガス浄化触媒。1. An exhaust gas purification catalyst containing oxygen for an internal combustion engine, which is a spinel type composite oxide containing at least one of Ni and Fe.
学式AB2O4(A,Bは金属元素)で記述される酸化物
であることを特徴とする内燃機関の酸素を含む排気ガス
浄化触媒。2. Purification of exhaust gas containing oxygen from an internal combustion engine, characterized by being an oxide containing at least one of Ni and Fe and represented by the chemical formula AB 2 O 4 (A and B are metallic elements). catalyst.
とも一つを有することを特徴とする内燃機関の酸素を含
む排気ガスから窒素酸化物を除去する装置。3. An apparatus for removing nitrogen oxides from an exhaust gas containing oxygen of an internal combustion engine, which comprises at least one of the catalysts according to claims 1 and 2.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6175118A JPH0838902A (en) | 1994-07-27 | 1994-07-27 | Exhaust gas purification catalyst and device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6175118A JPH0838902A (en) | 1994-07-27 | 1994-07-27 | Exhaust gas purification catalyst and device |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0838902A true JPH0838902A (en) | 1996-02-13 |
Family
ID=15990595
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP6175118A Pending JPH0838902A (en) | 1994-07-27 | 1994-07-27 | Exhaust gas purification catalyst and device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0838902A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002030924A (en) * | 2000-07-17 | 2002-01-31 | Nissan Diesel Motor Co Ltd | Exhaust emission control device for diesel engine |
| WO2013022359A1 (en) * | 2011-08-08 | 2013-02-14 | Uniwersytet Jagielloński | Catalyst for direct decomposition of nitric oxide and method of manufacturing the catalyst |
-
1994
- 1994-07-27 JP JP6175118A patent/JPH0838902A/en active Pending
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002030924A (en) * | 2000-07-17 | 2002-01-31 | Nissan Diesel Motor Co Ltd | Exhaust emission control device for diesel engine |
| WO2013022359A1 (en) * | 2011-08-08 | 2013-02-14 | Uniwersytet Jagielloński | Catalyst for direct decomposition of nitric oxide and method of manufacturing the catalyst |
| US9162216B2 (en) | 2011-08-08 | 2015-10-20 | Uniwersytet Jagiellonski | Catalyst for direct decomposition of nitric oxide and method of manufacturing the catalyst |
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