JPH07204510A - Catalyst to purify exhaust gas - Google Patents

Catalyst to purify exhaust gas

Info

Publication number
JPH07204510A
JPH07204510A JP6002129A JP212994A JPH07204510A JP H07204510 A JPH07204510 A JP H07204510A JP 6002129 A JP6002129 A JP 6002129A JP 212994 A JP212994 A JP 212994A JP H07204510 A JPH07204510 A JP H07204510A
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
nitrogen oxides
oxygen
mol
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP6002129A
Other languages
Japanese (ja)
Inventor
Satoru Kondo
知 近藤
Masahiro Watanabe
正広 渡邊
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.)
Tosoh Corp
Original Assignee
Tosoh 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 Tosoh Corp filed Critical Tosoh Corp
Priority to JP6002129A priority Critical patent/JPH07204510A/en
Publication of JPH07204510A publication Critical patent/JPH07204510A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To obtain a catalyst having excellent durability and low temp. activity to remove nitrogen oxides from oxygen-rich exhaust gas by constituting the catalyst of copper and solid acid produced by adding tungsten to zirconia and specifying the amts. of tungsten and zirconia of the compsn. CONSTITUTION:This catalyst to purify exhaust gas is used to remove nitrogen oxides and hydrocarbons from oxygen-rich exhaust gas containing nitrogen oxides, carbon monoxide, and hydrocarbons. The catalyst consists of copper and solid acid prepared by adding tungsten to zirconia, and the compsn. of the catalyst is 0.2-5.0mol% tungsten, 0.2-5.0mol% copper and 90-99.6mol% zirconia. Nitrogen oxides in oxygen-rich exhaust gas are removed by bringing the oxygen-rich exhaust gas containing nitrogen oxides, carbon monoxide and hydrocarbons into contact with the catalyst for purification of exhaust gas. The oxygen-rich exhaust gas to be purified is, for example, exhaust gas from an inner combustion engine such as of an automobile, especially in a large air-fuel ratio.

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、例えば自動車エンジン
等の内燃機関から排出される排気ガス中の窒素酸化物、
一酸化炭素及び炭化水素を除去する排気ガス浄化触媒に
関し、特に酸素過剰の燃焼排気ガスを浄化する触媒に関
するものである。
BACKGROUND OF THE INVENTION The present invention relates to nitrogen oxides in exhaust gas discharged from an internal combustion engine such as an automobile engine,
The present invention relates to an exhaust gas purifying catalyst that removes carbon monoxide and hydrocarbons, and more particularly to a catalyst that purifies combustion exhaust gas containing excess oxygen.

【0002】[0002]

【従来の技術】内燃機関から排出される排気ガス中の有
害物質である窒素酸化物、一酸化炭素及び炭化水素は例
えばPt,Rh,Pd等を担体上に担持させた三元触媒
により除去されている。しかしながらこのような三元触
媒では酸素が過剰に存在する場合には排気中の窒素酸化
物を還元除去することができないという欠点がある。す
なわち酸素が多く含まれるディーゼルエンジン排気ガス
中の窒素酸化物を浄化することが困難であり、また近
年、ガソリンエンジンにおいても低燃費化や排気炭酸ガ
ス低減の目的でガソリン濃度の希薄な条件で燃焼させる
リーンバーンエンジンが開発されているがこの排気ガス
は酸素過剰雰囲気であるためやはり三元触媒では窒素酸
化物を浄化することができない。
2. Description of the Related Art Nitrogen oxides, carbon monoxide and hydrocarbons which are harmful substances in exhaust gas discharged from an internal combustion engine are removed by a three-way catalyst having Pt, Rh, Pd, etc. supported on a carrier. ing. However, such a three-way catalyst has a drawback that nitrogen oxides in exhaust cannot be reduced and removed when oxygen is present in excess. In other words, it is difficult to purify nitrogen oxides in the exhaust gas of diesel engines that contain a large amount of oxygen, and in recent years, gasoline engines have also been burned under conditions of lean gasoline concentration for the purpose of reducing fuel consumption and reducing carbon dioxide emissions. A lean burn engine has been developed, but since this exhaust gas is in an oxygen excess atmosphere, nitrogen oxides cannot be purified with a three-way catalyst.

【0003】酸素過剰雰囲気中での浄化触媒として、銅
をイオン交換した結晶性アルミノシリケート触媒が有望
な触媒として注目されているが耐久性の点で問題を抱え
ている。
As a purifying catalyst in an oxygen excess atmosphere, a crystalline aluminosilicate catalyst in which copper is ion-exchanged has been attracting attention as a promising catalyst, but it has a problem in durability.

【0004】またジルコニアなどの固体酸触媒も酸素過
剰雰囲気中での浄化触媒として有効で耐久性も優れてい
るが、高い活性を示す温度域が500℃付近の高温であ
るという問題がある。
A solid acid catalyst such as zirconia is also effective as a purifying catalyst in an oxygen excess atmosphere and has excellent durability, but there is a problem that the temperature range showing high activity is a high temperature around 500 ° C.

【0005】[0005]

【発明が解決しようとする課題】本発明の目的は以上の
ような従来技術の問題点を解消するためになされたもの
であり、酸素過剰の排気ガスから窒素酸化物、一酸化炭
素及び炭化水素を除去する、耐久性に優れ、かつ低温度
域で活性を有する触媒を提供するものである。
SUMMARY OF THE INVENTION The object of the present invention is to solve the above-mentioned problems of the prior art, and to remove nitrogen oxides, carbon monoxide and hydrocarbons from oxygen-rich exhaust gas. The present invention provides a catalyst which is excellent in durability and has activity in a low temperature range.

【0006】[0006]

【課題を解決するための手段】本発明者らが検討当した
結果、ジルコニアにタングステンを添加した固体酸にさ
らに銅を添加すると、窒素酸化物、一酸化炭素及び炭化
水素を含む酸素過剰の排気ガスから、窒素酸化物、一酸
化炭素及び炭化水素を除去する触媒として、耐久性に優
れ、かつ低温度域で活性を有すことを見出だした。
Means for Solving the Problems As a result of studies by the present inventors, when copper is further added to a solid acid obtained by adding tungsten to zirconia, excess oxygen exhaust containing nitrogen oxides, carbon monoxide and hydrocarbons is exhausted. As a catalyst for removing nitrogen oxides, carbon monoxide and hydrocarbons from gas, it has been found that it has excellent durability and has activity in a low temperature range.

【0007】即ち、本発明はジルコニアにタングステン
を添加した固体酸及び銅からなり、その組成がタングス
テンが0.2〜5.0mol%、銅が0.2〜5.0m
ol%、ジルコニアが90〜99.6mol%の範囲で
あることを特徴とする、窒素酸化物、一酸化炭素及び炭
化水素を含む酸素過剰の排気ガスから、窒素酸化物、一
酸化炭素及び炭化水素を除去する排気ガス浄化触媒に関
するものである。
That is, the present invention comprises a solid acid obtained by adding tungsten to zirconia and copper, the composition of which is 0.2 to 5.0 mol% of tungsten and 0.2 to 5.0 m of copper.
nitrogen oxides, carbon monoxide and hydrocarbons from oxygen-rich exhaust gas containing nitrogen oxides, carbon monoxide and hydrocarbons, characterized in that the ol% and zirconia are in the range of 90 to 99.6 mol%. The present invention relates to an exhaust gas purifying catalyst for removing.

【0008】以下、本発明を詳細に説明する。The present invention will be described in detail below.

【0009】添加金属酸化物のうちタングステンの添加
量は0.2〜5.0mol%でなければならない。この
時のジルコニアにタングステンを添加した固体酸のハメ
ット指示薬による酸強度関数Hoは−8.2≦Ho≦+
3.3である。添加量が0.2mol%未満で、酸強度
がHo>+3.3の場合、炭化水素の燃焼のみが起こっ
て窒素酸化物の分解活性が低下し、また添加量が5mo
l%を越え、酸強度が−8.2>Hoの場合、炭化水素
の分解がうまく進行せず窒素酸化物の分解活性も低下す
る。また銅の添加量は0.2〜5.0mol%でなけれ
ばならない。添加量が5mol%を越える場合、炭化水
素の燃焼のみが起こって窒素酸化物の分解活性が低下
し、添加量が0.2mol%未満の場合、炭化水素の分
解がうまく進行せず窒素酸化物の分解活性も低下する。
Of the added metal oxide, the amount of tungsten added must be 0.2 to 5.0 mol%. At this time, the acid strength function Ho of the solid acid obtained by adding tungsten to zirconia by the Hammett indicator is −8.2 ≦ Ho ≦ +
3.3. When the added amount is less than 0.2 mol% and the acid strength is Ho> +3.3, only hydrocarbon combustion occurs and the decomposition activity of nitrogen oxides decreases, and the added amount is 5 mo.
When it exceeds 1% and the acid strength is -8.2> Ho, the decomposition of hydrocarbons does not proceed well and the decomposition activity of nitrogen oxides also decreases. Also, the amount of copper added must be 0.2 to 5.0 mol%. When the amount added exceeds 5 mol%, only hydrocarbon combustion occurs and the decomposition activity of nitrogen oxides decreases, and when the amount added is less than 0.2 mol%, hydrocarbon decomposition does not proceed well and nitrogen oxides do not progress. The decomposition activity of is also reduced.

【0010】本発明において添加される金属酸化物の状
態は固溶、担持のいずれでも良い。表面積については特
に制限はなく、より大きいことが望ましい。
The state of the metal oxide added in the present invention may be either solid solution or supported. There is no particular limitation on the surface area, and a larger surface area is desirable.

【0011】本発明の触媒の調製においてタングステン
を添加する場合には非晶質のジルコニアに対して添加す
る必要がある。結晶性のジルコニアに添加した場合には
効果を発揮しないためである。銅の添加については特に
制限はない。調製法はとくに限定されず、各種の方法が
利用できる。例えば、水酸化ジルコニウムに金属酸化物
を含浸担持、イオン交換等の方法で含有させることがで
きる。またジルコニウム塩と添加金属種の塩を含む水溶
液から共沈法などによって得ることもでき、有機金属塩
を用いたアルコキシド法などによっても得ることができ
る。またタングステン添加ジルコニウムに銅を含浸担
持、イオン交換等の方法で含有させ、触媒を得ることも
できる。
When tungsten is added in the preparation of the catalyst of the present invention, it is necessary to add it to amorphous zirconia. This is because when added to crystalline zirconia, no effect is exhibited. There is no particular limitation on the addition of copper. The preparation method is not particularly limited, and various methods can be used. For example, zirconium hydroxide can be incorporated with a metal oxide by a method such as impregnating and supporting, or ion exchange. It can also be obtained from an aqueous solution containing a zirconium salt and a salt of an added metal species by a coprecipitation method or the like, or by an alkoxide method using an organic metal salt or the like. Alternatively, the catalyst can be obtained by impregnating and supporting copper in the zirconium containing tungsten by a method such as impregnating and supporting, or ion exchange.

【0012】添加物の含浸担持、イオン交換は、水酸化
ジルコニウムを、添加金属塩を含む溶液に混合し攪拌し
た後、ろ過、乾燥し焼成することにより行われる。水酸
化ジルコニウムは市販品、あるいはジルコニウム塩を含
む溶液から沈殿法等により得られたものであっても良
い。焼成温度は、温度が高すぎるとWO3が凝集析出し
添加効果を発揮しないため850℃以下であることが好
ましい。金属塩の原料としては水酸化物、硝酸塩、硫酸
塩、塩化物、各種有機酸塩等が用い得る。
The impregnation, loading and ion exchange of the additive are carried out by mixing zirconium hydroxide with the solution containing the added metal salt, stirring, filtering, drying and firing. Zirconium hydroxide may be a commercially available product or may be obtained from a solution containing a zirconium salt by a precipitation method or the like. If the temperature is too high, WO 3 aggregates and precipitates and the effect of addition is not exhibited, so the firing temperature is preferably 850 ° C. or lower. As the raw material of the metal salt, hydroxide, nitrate, sulfate, chloride, various organic acid salts and the like can be used.

【0013】これらの方法は本発明による排気ガス浄化
触媒の調製方法を例示したものであり、本発明による触
媒は上記以外の方法により調製されたものを用いること
も可能である。
These methods exemplify the method for preparing the exhaust gas purifying catalyst according to the present invention, and the catalyst according to the present invention may be prepared by a method other than the above.

【0014】本発明の排気ガス浄化触媒は、単独でまた
は粘度鉱物等のバインダーと混合して成形し使用するこ
とができる。成形する際に用いられるバインダーとして
は例えばカオリン、アタパルカイト、モンモリロナイ
ト、ベントナイト、アロフェン、セピオライト等の粘度
鉱物を例示することができる。またさらに、コージェラ
イト製あるいは金属製等のハニカム状基材に本触媒をウ
オッシュコートして用いることも可能である。
The exhaust gas purifying catalyst of the present invention can be used alone or in the form of a mixture with a binder such as clay mineral. Examples of the binder used for molding include viscous minerals such as kaolin, attapulkite, montmorillonite, bentonite, allophane, and sepiolite. Furthermore, it is also possible to wash coat the present catalyst on a honeycomb-shaped substrate made of cordierite or metal.

【0015】本発明の排気ガス浄化触媒は酸素過剰の排
気ガスから窒素酸化物を除去するために用いられる。酸
素過剰排気ガス中の窒素酸化物の除去は、本発明の排気
ガス浄化触媒と、窒素酸化物、一酸化炭素および炭化水
素を含む酸素過剰排気ガスを接触させることにより行う
ことができる。本発明が対象とする酸素過剰の排気ガス
とは、排気ガス中に含まれる一酸化炭素、炭化水素及び
水素を完全に酸化するのに必要な酸素量よりも過剰な酸
素が含まれている排気ガスをいい、このような排気ガス
としては例えば、自動車等の内燃機関から排出される排
気ガス、特に空燃比が大きい状態での排気ガス等が具体
的に例示される。触媒の使用条件は特に限定しないが温
度範囲としては200℃〜850℃が好ましい。またS
Vについては1000h-1〜500000h-1であれば
よい。
The exhaust gas purifying catalyst of the present invention is used for removing nitrogen oxides from exhaust gas in excess of oxygen. Removal of nitrogen oxides in the oxygen excess exhaust gas can be performed by bringing the exhaust gas purification catalyst of the present invention into contact with the oxygen excess exhaust gas containing nitrogen oxides, carbon monoxide and hydrocarbons. Exhaust gas in excess of oxygen targeted by the present invention means exhaust gas containing oxygen in excess of the amount of oxygen required to completely oxidize carbon monoxide, hydrocarbons and hydrogen contained in the exhaust gas. Examples of such exhaust gas include exhaust gas discharged from an internal combustion engine such as an automobile, particularly exhaust gas in a state where the air-fuel ratio is large. The use conditions of the catalyst are not particularly limited, but the temperature range is preferably 200 ° C to 850 ° C. Also S
It may be a 1000h -1 ~500000h -1 for V.

【0016】[0016]

【発明の効果】本発明の排気ガス浄化触媒は酸素過剰雰
囲気での窒素酸化物、一酸化炭素及び炭化水素の浄化能
に優れており、したがって酸素が過剰なディーゼルエン
ジンの排気ガス、リーンバーンエンジンの排気ガス中の
窒素酸化物、一酸化炭素及び炭化水素の浄化を比較的低
温域でおこなうことができる。
The exhaust gas purifying catalyst of the present invention is excellent in the purifying ability of nitrogen oxides, carbon monoxide and hydrocarbons in an oxygen excess atmosphere, and therefore the exhaust gas of a diesel engine and lean burn engine in which oxygen is excessive. It is possible to purify nitrogen oxides, carbon monoxide, and hydrocarbons contained in the exhaust gas in a relatively low temperature range.

【0017】[0017]

【実施例】以下、本発明を実施例により更に詳細に説明
するが、本発明はこれら実施例に限定されるものではな
い。
EXAMPLES The present invention will now be described in more detail with reference to examples, but the present invention is not limited to these examples.

【0018】実施例1<触媒1> 6Nアンモニア水溶液500mlに1mol/リットル
のZrOCl2水溶液200mlを滴下して水酸化物沈
殿を得た。この沈殿を100℃で乾燥した後、この水酸
化物10gを、Cu(NO32・3H2O:0.15g
とWO3:0.15gをアンモニア水に溶解し、pHを
9.0に調整した溶液に混合、撹拌した後、濾過して1
00℃で乾燥し、800℃で2時間焼成し、触媒組成C
uO:1mol%、WO3:1mol%、ZrO2:98
mol%の触媒を調製した。触媒のハメット指示薬によ
る酸強度関数Hoは+1.5であった。
Example 1 <Catalyst 1> 200 ml of a 1 mol / liter ZrOCl 2 aqueous solution was added dropwise to 500 ml of a 6N ammonia aqueous solution to obtain a hydroxide precipitate. After drying this precipitate at 100 ° C., 10 g of this hydroxide was added to Cu (NO 3 ) 2 .3H 2 O: 0.15 g.
And WO 3 (0.15 g) were dissolved in ammonia water, mixed with a solution whose pH was adjusted to 9.0, stirred, and then filtered to 1
Dry at 00 ° C and calcine at 800 ° C for 2 hours to obtain catalyst composition C
uO: 1 mol%, WO 3 : 1 mol%, ZrO 2 : 98
A mol% catalyst was prepared. The acid strength function Ho by the Hammett indicator of the catalyst was +1.5.

【0019】実施例2<触媒2> 6Nアンモニア水溶液500mlに1mol/リットル
のZrOCl2水溶液200mlを滴下して水酸化物沈
殿を得た。この沈殿を100℃で乾燥した後、この水酸
化物10gを、Cu(NO32・3H2O:0.08g
とWO3:0.15gをアンモニア水に溶解し、pHを
9.0に調整した溶液に混合、撹拌した後、濾過して1
00℃で乾燥し、800℃で2時間焼成し、触媒組成C
uO:0.5mol%、WO3:1mol%、ZrO2
98.5mol%の触媒を調製した。触媒のハメット指
示薬による酸強度関数Hoは+1.5であった。
Example 2 <Catalyst 2> 200 ml of a 1 mol / liter ZrOCl 2 aqueous solution was dropped into 500 ml of a 6N ammonia aqueous solution to obtain a hydroxide precipitate. After drying the precipitate at 100 ° C., 10 g of this hydroxide was added to Cu (NO 3 ) 2 .3H 2 O: 0.08 g
And WO 3 (0.15 g) were dissolved in ammonia water, mixed with a solution whose pH was adjusted to 9.0, stirred, and then filtered to 1
Dry at 00 ° C and calcine at 800 ° C for 2 hours to obtain catalyst composition C
uO: 0.5 mol%, WO 3 : 1 mol%, ZrO 2 :
A 98.5 mol% catalyst was prepared. The acid strength function Ho by the Hammett indicator of the catalyst was +1.5.

【0020】比較例1<比較触媒1> 6Nアンモニア水溶液500mlに1mol/リットル
のZrOCl2水溶液200mlを滴下して水酸化物沈
殿を得た。この沈殿を100℃で乾燥した後、800℃
で2時間焼成し、触媒組成ZrO2:100mol%の
触媒を調製した。触媒のハメット指示薬による酸強度関
数Hoは+6.8であった。
Comparative Example 1 <Comparative Catalyst 1> 200 ml of a 1 mol / liter ZrOCl 2 aqueous solution was dropped into 500 ml of a 6N ammonia aqueous solution to obtain a hydroxide precipitate. After drying this precipitate at 100 ℃, 800 ℃
The mixture was calcined for 2 hours to prepare a catalyst having a catalyst composition of ZrO 2 : 100 mol%. The acid strength function Ho by the Hammett indicator of the catalyst was +6.8.

【0021】比較例2<比較触媒2> 6Nアンモニア水溶液500mlに1mol/リットル
のZrOCl2水溶液200mlを滴下して水酸化物沈
殿を得た。この沈殿を100℃で乾燥した後、この水酸
化物10gを、Cu(NO32・3H2O:0.15g
を溶解し、pHを9.0に調整した溶液に混合、撹拌し
た後、濾過して100℃で乾燥し、800℃で2時間焼
成し、触媒組成CuO:1mol%、ZrO2:99m
ol%の触媒を調製した。触媒のハメット指示薬による
酸強度関数Hoは+6.8であった。
Comparative Example 2 <Comparative Catalyst 2> 200 ml of a 1 mol / liter ZrOCl 2 aqueous solution was dropped into 500 ml of a 6N ammonia aqueous solution to obtain a hydroxide precipitate. After drying this precipitate at 100 ° C., 10 g of this hydroxide was added to Cu (NO 3 ) 2 .3H 2 O: 0.15 g.
Was dissolved, mixed with a solution whose pH was adjusted to 9.0, stirred, filtered, dried at 100 ° C., and calcined at 800 ° C. for 2 hours to obtain a catalyst composition CuO: 1 mol%, ZrO 2 : 99 m.
An ol% catalyst was prepared. The acid strength function Ho by the Hammett indicator of the catalyst was +6.8.

【0022】比較例3<比較触媒3> 6Nアンモニア水溶液500mlに1mol/リットル
のZrOCl2水溶液200mlを滴下して水酸化物沈
殿を得た。この沈殿を100℃で乾燥した後、この水酸
化物10gを、WO3を0.37gアンモニア水に溶解
し、pHを9.0に調整した溶液に混合、撹拌した後、
濾過して100℃で乾燥し、800℃で2時間焼成し、
触媒組成WO3:2.5mol%、ZrO2:97.5m
ol%の触媒を調製した。触媒のハメット指示薬による
酸強度関数Hoは+1.5であった。
Comparative Example 3 <Comparative Catalyst 3> 200 ml of a 1 mol / liter ZrOCl 2 aqueous solution was added dropwise to 500 ml of a 6N ammonia aqueous solution to obtain a hydroxide precipitate. After drying this precipitate at 100 ° C., 10 g of this hydroxide was mixed with 0.37 g of WO 3 dissolved in ammonia water and mixed with a solution whose pH was adjusted to 9.0.
Filter, dry at 100 ° C, calcine at 800 ° C for 2 hours,
Catalyst composition WO 3 : 2.5 mol%, ZrO 2 : 97.5 m
An ol% catalyst was prepared. The acid strength function Ho by the Hammett indicator of the catalyst was +1.5.

【0023】比較例4<比較触媒4> 6Nアンモニア水溶液500mlに1mol/リットル
のZrOCl2水溶液200mlを滴下して水酸化物沈
殿を得た。この沈殿を100℃で乾燥した後、この水酸
化物10gを、Cu(NO32・3H2O:0.16g
とWO3:1.11gをアンモニア水に溶解し、pHを
9.0に調整した溶液に混合、撹拌した後、濾過して1
00℃で乾燥し、800℃で2時間焼成し、触媒組成C
uO:1mol%、WO3:7mol%、ZrO2:92
mol%の触媒を調製した。触媒の酸強度関数Hoは−
13.75であった。
Comparative Example 4 <Comparative Catalyst 4> 200 ml of a 1 mol / liter ZrOCl 2 aqueous solution was added dropwise to 500 ml of a 6N ammonia aqueous solution to obtain a hydroxide precipitate. After drying this precipitate at 100 ° C., 10 g of this hydroxide was added to Cu (NO 3 ) 2 .3H 2 O: 0.16 g
And WO 3 (1.11 g) were dissolved in ammonia water, mixed with a solution whose pH was adjusted to 9.0, stirred and then filtered to 1
Dry at 00 ° C and calcine at 800 ° C for 2 hours to obtain catalyst composition C
uO: 1 mol%, WO 3 : 7 mol%, ZrO 2 : 92
A mol% catalyst was prepared. The acid strength function Ho of the catalyst is −
It was 13.75.

【0024】比較例5<比較触媒5> 6Nアンモニア水溶液500mlに1mol/リットル
のZrOCl2水溶液200mlを滴下して水酸化物沈
殿を得た。この沈殿を100℃で乾燥した後、この水酸
化物10gを、Cu(NO32・3H2O:1.15g
とWO3:0.16gをアンモニア水に溶解し、pHを
9.0に調整した溶液に混合、撹拌した後、濾過して1
00℃で乾燥し、800℃で2時間焼成し、触媒組成C
uO:7mol%、WO3:1mol%、ZrO2:92
mol%の触媒を調製した。触媒のハメット指示薬によ
る酸強度関数Hoは+1.5であった。
Comparative Example 5 <Comparative Catalyst 5> 200 ml of a 1 mol / liter ZrOCl 2 aqueous solution was added dropwise to 500 ml of a 6N ammonia aqueous solution to obtain a hydroxide precipitate. After drying this precipitate at 100 ° C., 10 g of this hydroxide was added to Cu (NO 3 ) 2 .3H 2 O: 1.15 g.
And WO 3: the 0.16g was dissolved in aqueous ammonia, mixing the solution adjusted to pH 9.0, stirred and filtered 1
Dry at 00 ° C and calcine at 800 ° C for 2 hours to obtain catalyst composition C
uO: 7 mol%, WO 3 : 1 mol%, ZrO 2 : 92
A mol% catalyst was prepared. The acid strength function Ho by the Hammett indicator of the catalyst was +1.5.

【0025】実施例3 実施例1,2により得られた触媒をプレス成形後破砕し
て12〜20メッシュに整粒し、常圧固定床流通反応装
置により表1に示す組成のガスを用いてSV=2500
-1においてNO浄化率を測定した。その結果を表2に
示す。
Example 3 The catalysts obtained in Examples 1 and 2 were press-molded, then crushed and sized to 12 to 20 mesh, and the gas having the composition shown in Table 1 was used by a normal pressure fixed bed flow reactor. SV = 2500
The NO purification rate was measured at h -1 . The results are shown in Table 2.

【0026】[0026]

【表1】 [Table 1]

【0027】なおNO浄化率は次の式により示される。The NO purification rate is expressed by the following equation.

【0028】NO浄化率(%)=(NOin−NOou
t)/NOin×100 NOin :固定床反応管入口NO濃度 NOout:固定床反応管出口NO濃度
NO purification rate (%) = (NOin-NOou
t) / NOin × 100 NOin: Fixed bed reaction tube inlet NO concentration NOout: Fixed bed reaction tube outlet NO concentration

【0029】[0029]

【表1】 [Table 1]

【0030】比較例4 実施例3と同じ条件で比較例1〜5により得られた触媒
の浄化率を測定した。その結果を表3に示す。
Comparative Example 4 Purification rates of the catalysts obtained in Comparative Examples 1 to 5 were measured under the same conditions as in Example 3. The results are shown in Table 3.

【0031】[0031]

【表1】 [Table 1]

───────────────────────────────────────────────────── 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 53/36 104 A ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location B01D 53/36 104 A

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】ジルコニアにタングステンを添加した固体
酸及び銅からなり、その組成がタングステンが0.2〜
5.0mol%、銅が0.2〜5.0mol%、ジルコ
ニアが90〜99.6mol%の範囲であることを特徴
とする、窒素酸化物、一酸化炭素及び炭化水素を含む酸
素過剰の排気ガスから、窒素酸化物、一酸化炭素及び炭
化水素を除去する排気ガス浄化触媒。
1. A solid acid obtained by adding tungsten to zirconia and copper, the composition of which is about 0.2 to 20% tungsten.
5.0 mol%, 0.2 to 5.0 mol% of copper, 90 to 99.6 mol% of zirconia in the range of excess oxygen containing nitrogen oxides, carbon monoxide and hydrocarbons. An exhaust gas purification catalyst that removes nitrogen oxides, carbon monoxide, and hydrocarbons from gas.
JP6002129A 1994-01-13 1994-01-13 Catalyst to purify exhaust gas Pending JPH07204510A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6002129A JPH07204510A (en) 1994-01-13 1994-01-13 Catalyst to purify exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6002129A JPH07204510A (en) 1994-01-13 1994-01-13 Catalyst to purify exhaust gas

Publications (1)

Publication Number Publication Date
JPH07204510A true JPH07204510A (en) 1995-08-08

Family

ID=11520738

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6002129A Pending JPH07204510A (en) 1994-01-13 1994-01-13 Catalyst to purify exhaust gas

Country Status (1)

Country Link
JP (1) JPH07204510A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6645439B2 (en) 1998-05-27 2003-11-11 Johnson Matthey Japan Ltd. Exhaust gas clean-up catalyst
JP2015139719A (en) * 2014-01-27 2015-08-03 株式会社豊田中央研究所 Three-way catalyst, and method for cleaning exhaust gas by using the same

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6645439B2 (en) 1998-05-27 2003-11-11 Johnson Matthey Japan Ltd. Exhaust gas clean-up catalyst
JP2015139719A (en) * 2014-01-27 2015-08-03 株式会社豊田中央研究所 Three-way catalyst, and method for cleaning exhaust gas by using the same

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