JPH02122830A - Catalyst for removal of nitrogen oxide - Google Patents

Catalyst for removal of nitrogen oxide

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Publication number
JPH02122830A
JPH02122830A JP63277694A JP27769488A JPH02122830A JP H02122830 A JPH02122830 A JP H02122830A JP 63277694 A JP63277694 A JP 63277694A JP 27769488 A JP27769488 A JP 27769488A JP H02122830 A JPH02122830 A JP H02122830A
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JP
Japan
Prior art keywords
catalyst
temperature
group
baked
oxides
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
JP63277694A
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Japanese (ja)
Other versions
JP2689147B2 (en
Inventor
Masafumi Yoshimoto
吉本 雅文
Tadao Nakatsuji
忠夫 仲辻
Kazuhiko Nagano
永野 一彦
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.)
Sakai Chemical Industry Co Ltd
Original Assignee
Sakai Chemical Industry Co Ltd
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Filing date
Publication date
Application filed by Sakai Chemical Industry Co Ltd filed Critical Sakai Chemical Industry Co Ltd
Priority to JP63277694A priority Critical patent/JP2689147B2/en
Priority to EP89202496A priority patent/EP0362960A3/en
Priority to US07/417,422 priority patent/US5128305A/en
Publication of JPH02122830A publication Critical patent/JPH02122830A/en
Priority to US07/518,560 priority patent/US5049364A/en
Application granted granted Critical
Publication of JP2689147B2 publication Critical patent/JP2689147B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Catalysts (AREA)

Abstract

PURPOSE:To permit an efficient cleavage of nitrogen oxides in a gas in the presence of CO by forming a catalyst of the baked product of (a) the oxides of alkali metal (b) Al2O3, SiO2, etc., and (c) platinum group metal or its oxide. CONSTITUTION:A mixture of alkali metal or the oxides of alkaline earth metal and a metallic oxide selected from Al2O3, SiO2, ZrO2, Fe2O3, TiO2, etc., after formation by extrusion molding, is baked at a temperature of 300-800 deg.C. Such baked product is immersed in the water-soluble salt of any one of Ru, Rh, Pd, Ag, Pt and Au and, after drying, is baked at a temperature of 300-800 deg.C and baked again, as required, in a reducing atmosphere to form a catalyst. This catalyst can effect the reductive cleavage of nitrogen oxides for removal from exhaust gases with the addition of a reducing agent CO thereto at the gas temperature of 300-800 deg.C.

Description

【発明の詳細な説明】 産業上の利用分解 本発明は、排ガス中に含まれる窒素酸化物を除去する方
法に関する。
DETAILED DESCRIPTION OF THE INVENTION Industrial Application Decomposition The present invention relates to a method for removing nitrogen oxides contained in exhaust gas.

従来の技所 従来排ガス中に含まれる窒素酸化物は、■窒素酸化物を
酸化しアルカリ吸収させる方法、■窒素酸化物をNH3
、【■2、CO等の還元剤により、N2とする方法など
により除去されてきた。これらの方法は■の場合排水処
理が必要となり、■の場合NH3等の還元剤が必要であ
るため処理コストが高く、特にNH3とSOxとの反応
による塩類生成による活性低下があるなどの問題を有し
てきた。またCOを還元剤とする場合これらの問題はな
いが、0□の共存下では、COと02が反応し、効率的
に還元することがてきないという問題点を有してきた。
Nitrogen oxides contained in exhaust gas from conventional laboratories can be removed by: ■ oxidizing nitrogen oxides and absorbing alkali; ■ converting nitrogen oxides to NH3
, [■2, CO and other reducing agents have been used to remove N2. These methods require wastewater treatment in the case of (■), and require a reducing agent such as NH3 in the case of (■), resulting in high treatment costs.In particular, there are problems such as a decrease in activity due to the formation of salts due to the reaction between NH3 and SOx. I have had it. In addition, when CO is used as a reducing agent, these problems do not occur, but in the coexistence of 0□, CO and 02 react, making it impossible to reduce efficiently.

・11 ゛ ′よる問題点 本発明は、上記の欠点を解決し、還元剤COを添加し窒
素酸化物を高効率に選択分解することができる触媒にか
かるものである。
Problems due to 11' The present invention solves the above-mentioned drawbacks and relates to a catalyst that can selectively decompose nitrogen oxides with high efficiency by adding a reducing agent CO.

ルIケ六′□ 7・ の−丑 本発明にかかる触媒は、排ガス中に含有する窒素酸化物
をCOの共存下で (a)アルカリ金属及びもしくはアルカリ土類金属酸化
物と (b)A I 203.5in2、ZrO2、Fe2O
3、TiO2、WO3、MoO3,51102、B1□
03、ZnOから選択される1種以上の金属酸化物と及
び (c)RuSRh、 Pd、 Ag、 P t、 Au
から選択される1種以上の金属もしくは、金属酸化物と
からなる触媒と接触させ、窒素酸化物をN2と002に
分解することができる触媒である。
The catalyst according to the present invention converts nitrogen oxides contained in exhaust gas into (a) alkali metal and/or alkaline earth metal oxides and (b) A I 203.5in2, ZrO2, Fe2O
3, TiO2, WO3, MoO3, 51102, B1□
03, one or more metal oxides selected from ZnO, and (c) RuSRh, Pd, Ag, Pt, Au
This is a catalyst that can decompose nitrogen oxides into N2 and 002 when brought into contact with a catalyst consisting of one or more metals or metal oxides selected from the following.

本触媒は(a)  (b)と(C)から選択される触媒
成分もしくはそれらの前駆体を用いて、公知の方法によ
り調整することができる。
The present catalyst can be prepared by a known method using a catalyst component selected from (a), (b) and (C) or a precursor thereof.

例えば (1)アルカリ土類金属酸化物(マグネシア、カルシア
、酸化ストロンチウムなど)と(b)群から選択される
酸化物を予め混合し、任意の成形方法(押出成形、打錠
成形、球状成形など)により成形しその後300℃〜8
00℃の温度条件で焼成し、これを(C)群から選択さ
れる金属及びもしくはアルカリ金属塩水溶ン夜に浸漬し
、乾燥後300°C〜800°Cの温度条件で焼成する
。さらに必要に応じて還元雰囲気中で焼成する。
For example, (1) an alkaline earth metal oxide (magnesia, calcia, strontium oxide, etc.) and an oxide selected from group (b) are mixed in advance, and any molding method (extrusion molding, tablet molding, spherical molding, etc.) is used. ) and then molded at 300℃~8
This is baked at a temperature of 300°C to 800°C, immersed in an aqueous solution of metal and/or alkali metal salt selected from group (C), and dried at a temperature of 300°C to 800°C. Further, if necessary, it is fired in a reducing atmosphere.

(2)アルカリ土類金属塩と(b)群から選択される金
属の塩を水などに溶解しこれにアルカリ(アンモニア、
水酸化ナトリウムなと)など沈澱剤を加え沈澱を生成し
、これを乾燥し、その後300℃〜800℃の温度条件
で焼成し粉砕し、任意の成形方法(押出成形、打錠成形
、球状成形など)により成形し、さらに必要に応じて3
00°C〜800℃の温度条1′1て焼成し、これを(
C)群から選択される金属及びもしくはアルカリ金属塩
水溶液に浸漬し、乾燥後300℃〜800℃の温度条件
で焼成する。さらに必要に応して還元雰囲気中で焼成す
る。
(2) Dissolve an alkaline earth metal salt and a salt of a metal selected from group (b) in water, etc., and add alkali (ammonia,
A precipitant such as sodium hydroxide is added to form a precipitate, which is dried, then calcined and pulverized at a temperature of 300°C to 800°C. etc.), and if necessary, 3
It is fired at a temperature of 00°C to 800°C.
It is immersed in a metal and/or alkali metal salt aqueous solution selected from group C), dried, and then fired at a temperature of 300°C to 800°C. Further, if necessary, it is fired in a reducing atmosphere.

(3)アルカリ金属塩、(b)群から選択される金属塩
及び(C)群から選択される金属塩を水などに溶解し、
これにアルカリ(アンモニア、水酸化ナトリウムなど)
など沈澱剤を加え、沈澱を生成し、これを乾燥し、その
後300℃〜800℃の温度条件で焼成する。これを粉
砕し任意の成形方法(押出成形、打錠成形、球状成形な
ど)により成形し、さらに必要に応じて300℃〜80
0℃の温度条件で焼成する。さらに場合によってはこれ
を還元雰囲気中で焼成してもよい。
(3) Dissolving an alkali metal salt, a metal salt selected from group (b), and a metal salt selected from group (C) in water or the like,
Add to this an alkali (ammonia, sodium hydroxide, etc.)
A precipitant such as the like is added to form a precipitate, which is dried and then calcined at a temperature of 300°C to 800°C. This is crushed and molded by any molding method (extrusion molding, tablet molding, spherical molding, etc.), and further heated to 300°C to 800°C as necessary.
Fired at a temperature of 0°C. Furthermore, depending on the case, this may be fired in a reducing atmosphere.

これらの方法は本発明触媒の調整方法を例示したもので
あり、これに特定されるものではなく、触媒成分が同じ
ものであれば同等の効果が得られる。
These methods are illustrative of methods for preparing the catalyst of the present invention, and are not limited thereto, and equivalent effects can be obtained if the catalyst components are the same.

本発明に用いることができる(a)群の金属酸化物は酸
化マグネシウム、酸化カルシウム、酸化ストロンチウム
であり、(a)群の前駆体は水酸化マグネシウム、水酸
化カルシウム、水酸化ストロンチウム、水酸化バリウム
などの水酸化物、硝酸マグ才、シウム、硝酸カルシウム
、硝酸ストロンチウム、硝酸バリウムなと水溶性塩なと
である。なおこれらの沈澱剤としては炭酸塩あるいは水
酸化ナトリウムなとのアルカリか好ましい。
The metal oxides of group (a) that can be used in the present invention are magnesium oxide, calcium oxide, and strontium oxide, and the precursors of group (a) are magnesium hydroxide, calcium hydroxide, strontium hydroxide, and barium hydroxide. Hydroxides such as nitrate, sium, calcium nitrate, strontium nitrate, barium nitrate, and water-soluble salts. The precipitating agent is preferably an alkali such as carbonate or sodium hydroxide.

また本発明に用いることができる(b)群の金属酸化物
はAl2O3、S i O、、、ZrO□、Fe、、0
3、TiO2、WO3、MoO3、SnO2、B12O
3、ZnOから選択される1種以」二の金属酸化物であ
り、好ましい原料である(b)群の前駆体としては、水
酸化物、硝酸塩などの水溶性塩を挙げることができる。
Further, metal oxides of group (b) that can be used in the present invention include Al2O3, SiO, , ZrO□, Fe, 0
3. TiO2, WO3, MoO3, SnO2, B12O
Precursors of group (b), which are one or more metal oxides selected from 3. ZnO and are preferred raw materials, include water-soluble salts such as hydroxides and nitrates.

さらに(C)群の金属もしくは金属酸化物としては、前
駆体を用いることが好ましく塩化ルテニウム、硝酸ロジ
ウム、塩化パラジウム、硝酸銀、塩化白金酸、塩化金酸
などの水溶性塩を挙げることができる。またこれらの成
分以外にチタニア、アルミナ、シリカなどの公知の担体
成分、粘土などの成形助剤成分、ガラスセンイなどの補
強剤を添加してもよい。
Furthermore, as the metal or metal oxide of group (C), it is preferable to use a precursor, and examples thereof include water-soluble salts such as ruthenium chloride, rhodium nitrate, palladium chloride, silver nitrate, chloroplatinic acid, and chloroauric acid. In addition to these components, known carrier components such as titania, alumina, and silica, molding aid components such as clay, and reinforcing agents such as glass fiber may be added.

しカルこれらの成分の総量は触媒成分中の50%以下と
することが好ましい。
The total amount of these components is preferably 50% or less in the catalyst components.

本発明にかかる触媒は、(a)群、(b)群及び(c)
群とからなるがこれらの好ましい組成比は原子比で(a
)群:(b)群:(C)群が90〜50:5〜50:0
.01〜10あり、より好ましくは90〜75:10〜
25:0.1〜5である。本発明者らはNOxの接触分
解の素反応が 2NO+2e  −+   2NO−(1)2NO−+
CO+   N、、+2CO’−(2)2CO−−Co
□+2e   (3) CO2→  CO2↑    (4) からなり、(a)群は(1) (2)の反応に、(b)
群は(3)の反応に、(c)群は(4)の反応に関与し
ていると考えている。これらのそれぞれの反応速度への
寄与は定かではないが、これらの原子比において、最も
還元分解活性を示す結果となった。
The catalyst according to the present invention comprises group (a), group (b) and group (c).
The preferred composition ratio of these groups is (a
) group: (b) group: (C) group is 90-50:5-50:0
.. 01-10, more preferably 90-75:10
25:0.1-5. The present inventors found that the elementary reaction of catalytic decomposition of NOx is 2NO+2e −+ 2NO−(1)2NO−+
CO+ N,,+2CO'-(2)2CO--Co
□+2e (3) CO2→ CO2↑ (4) Group (a) is the reaction of (1) (2), (b)
We believe that group (c) is involved in reaction (3) and group (c) is involved in reaction (4). Although the contribution of each of these to the reaction rate is unclear, the results showed the highest reductive decomposition activity at these atomic ratios.

本発明の触媒が還元分解活性を示す温度は300℃〜8
00°Cである。また好ましい温度は400〜600℃
である。この温度において本発明触媒は、5V=500
〜50000において使用することができる。
The temperature at which the catalyst of the present invention exhibits reductive decomposition activity is 300°C to 8°C.
It is 00°C. The preferred temperature is 400-600℃
It is. At this temperature, the catalyst of the present invention has a voltage of 5V=500
~50,000 can be used.

発明の効果 以上の様に本発明によれば(a)群(b)群及び(c)
群より選ばれた触媒成分を含有する触媒を用いることに
よって、排ガス温度が300℃〜800℃の温度域にお
いて窒素酸化物を還元剤COを添加し、還元分解除去す
ることが可能となったのである。
As described above, according to the present invention, group (a), group (b), and group (c)
By using a catalyst containing a catalyst component selected from the group, it has become possible to reduce and decompose nitrogen oxides in the exhaust gas temperature range of 300°C to 800°C by adding a reducing agent CO. be.

以下に実施例とともに比較例を挙げて本発明を説明する
が、本発明はこれらの実施例により何ら限定されるもの
ではない。
The present invention will be explained below by giving Examples and Comparative Examples, but the present invention is not limited to these Examples in any way.

実施例1゜ 硝酸マグネシウム、硝酸アルミニウムを各々酸化物基準
で90g、9g秤量しこれを1免のイオン交換水中に溶
解した。この水溶液中に充分撹拌を行ないながら、炭酸
ソーダーをpH7,0となるまで添加し中和反応を終了
した。(中和時間1時間)その後30分熟成後ろ過水洗
を行ない100℃で18時間乾燥後500℃3時間焼成
した。この焼成物をスクリーンが0.5mmφであるサ
ンプルミルにて粉砕した。この粉砕物を50g、水20
0」9中に投入し充分撹拌を行なったスラリー中に空隙
率81%、ピッチ4mmのセラミックファイバー製コル
ゲート状ハニカムを浸漬し、Mg O−A l 203
を該ハニカムに担持した。その担持率は143%であっ
た。これを常温通風乾燥後100℃18時間乾燥した。
Example 1 Magnesium nitrate and aluminum nitrate were weighed in an amount of 90 g and 9 g, respectively, based on their oxides, and dissolved in 1 cup of ion-exchanged water. Sodium carbonate was added to this aqueous solution with sufficient stirring until the pH reached 7.0 to complete the neutralization reaction. (Neutralization time: 1 hour) Thereafter, the mixture was aged for 30 minutes, washed with water, dried at 100°C for 18 hours, and then calcined at 500°C for 3 hours. This fired product was pulverized using a sample mill with a screen of 0.5 mmφ. 50g of this crushed material, 20g of water
A corrugated honeycomb made of ceramic fibers with a porosity of 81% and a pitch of 4 mm was immersed in the slurry that had been poured into a slurry of Mg O-Al 203 and thoroughly stirred.
was supported on the honeycomb. The loading rate was 143%. This was air-dried at room temperature and then dried at 100° C. for 18 hours.

この乾燥物を塩化金酸水溶液(Auとして33g/見)
中に浸漬し、常温通風乾燥後100℃18時間乾燥し、
500℃3時間焼成した。
This dried material was dissolved in an aqueous solution of chloroauric acid (33 g/view as Au).
After drying at room temperature with ventilation, drying at 100°C for 18 hours,
It was fired at 500°C for 3 hours.

実施例2゜ 硝酸アルミニウム、硝酸チタニルを各々酸化物基準で5
0g、50g秤量し、これを1見のイオン交換水中に溶
解した。この水溶液中に充分撹拌を行ないながらアンモ
ニアを吹き込みpH7,0として中和反応を終了した。
Example 2 Aluminum nitrate and titanyl nitrate were each 5
0g and 50g were weighed out and dissolved in ion-exchanged water. Ammonia was blown into this aqueous solution with sufficient stirring to adjust the pH to 7.0 and complete the neutralization reaction.

(中和時間1時間)その後30分熟成後ろ過水洗を行な
い、100°Cて18時間乾燥後600℃3時間焼成し
た。この焼成物をスクリーンが0.5mmφであるサン
プルミルにて粉砕した。この粉砕物50gと水酸化マグ
ネシウムを650℃“1時間焼成したマグネシア(比表
面積53m2/g)50gを水400Jに投入し、遊星
ミルにて30分分間式粉砕を行なった。このスラリー中
に空隙率81%ピッチ4mmのセラミックファイバー製
コルゲート状ハニカムを浸?貴し、Mg0−Al2O2
−Ti02を該ハニカムに担持した。その担持率は15
6%であった。以下実施例Iと同様にして触媒をigた
(Neutralization time: 1 hour) Thereafter, the mixture was aged for 30 minutes, washed with water, dried at 100°C for 18 hours, and then fired at 600°C for 3 hours. This fired product was pulverized using a sample mill with a screen of 0.5 mmφ. 50 g of this pulverized material and 50 g of magnesia (specific surface area 53 m2/g) obtained by calcining magnesium hydroxide at 650°C for 1 hour were added to 400 J of water and pulverized for 30 minutes in a planetary mill. Immerse a corrugated honeycomb made of ceramic fiber with a ratio of 81% and a pitch of 4 mm, Mg0-Al2O2
-Ti02 was supported on the honeycomb. Its carrying rate is 15
It was 6%. A catalyst was prepared in the same manner as in Example I.

実施例3゜ 実施例2の方法において、MgOとA1203−TiO
2を各々酸化物基準で75gと25g(実施例3−1)
及び25gと75g(実施例3−2)とした。
Example 3 In the method of Example 2, MgO and A1203-TiO
75g and 25g of 2 on an oxide basis (Example 3-1)
and 25g and 75g (Example 3-2).

実施例4゜ 実施例2の方法において、塩化金酸水溶ンα濃度をAu
としてIG5g/Q、とじた。
Example 4 In the method of Example 2, the concentration of aqueous chloroauric acid α was changed to
IG5g/Q, closed.

実施例5゜ 実施例2の方法において、塩化金酸水溶液に替えて塩化
白金酸水溶液を用いた。この時Pt濃度を16g/免(
実施例55−1)33/見(実施例55−2)66/免
(実施例5−3)とした。
Example 5 In the method of Example 2, a chloroplatinic acid aqueous solution was used in place of the chloroauric acid aqueous solution. At this time, the Pt concentration was reduced to 16g/min (
Example 55-1) 33/min (Example 55-2) 66/min (Example 5-3).

実施例6゜ 実施例2の方法において、塩化金酸水溶液に替えて塩化
ルテニウム水溶液(Ruとして33g/見)を用いた。
Example 6 In the method of Example 2, a ruthenium chloride aqueous solution (33 g/ml as Ru) was used in place of the chloroauric acid aqueous solution.

実施例7゜ 実施例2の方法において塩化白金酸水溶液に替えて硝酸
銀水溶液(A g 20として71g/見)を用いた。
Example 7 In the method of Example 2, a silver nitrate aqueous solution (71 g/stu as A g 20) was used in place of the chloroplatinic acid aqueous solution.

実施例8゜ 水酸化ジルコニウムとメタタングステン故アンモニウム
水溶液酸化物換算で85gと15g秤量し、水を加え充
分混練後100℃18時間乾燥し700℃にて3時間焼
成した。この焼成物をスクリーンが0.5mmφである
サンプルミルにて粉砕した。この粉砕物50gと実施例
2において用いたマグネシアを用いて以下実施例2と同
様にして触媒を得た。
Example 8 Aqueous solutions of zirconium hydroxide and metatungsten ammonium (85 g and 15 g) were weighed in terms of oxide, water was added, and the mixtures were sufficiently kneaded, dried at 100°C for 18 hours, and fired at 700°C for 3 hours. This fired product was pulverized using a sample mill with a screen of 0.5 mmφ. A catalyst was obtained in the same manner as in Example 2 using 50 g of this pulverized material and the magnesia used in Example 2.

実施例9゜ 8産化学製スノーテックスOとメタチタン酸ゾル(メタ
チタン酸を硝酸により解膠したもの)とを酸化物換算で
50g、50g秤量し、充分混合した後100℃18時
間乾燥し700℃3時間焼成した。この焼成物を実施例
2同様に粉砕した。この粉砕物50gと塩基性炭酸カル
シウムを650℃1時間焼成したカルシア(比表面積4
6m2/g)50gを用い以下実施例2と同様にして触
媒を得た。
Example 9 Weighed 50g of Snowtex O manufactured by 8 San Kagaku and metatitanic acid sol (metatatitanic acid peptized with nitric acid) in terms of oxide, mixed thoroughly, dried at 100°C for 18 hours, and then heated to 700°C. It was baked for 3 hours. This fired product was pulverized in the same manner as in Example 2. Calcia (specific surface area: 4
A catalyst was obtained in the same manner as in Example 2 using 50 g of 6m2/g).

実施例10゜ 実施例9の方法において塩化白金酸に替えて塩化パラジ
ウム水溶液を用いた。
Example 10° In the method of Example 9, an aqueous palladium chloride solution was used in place of chloroplatinic acid.

実施例11゜ 実施例9の方法において塩化白金酸に替えて硝酸ロジウ
ム水溶液を用いた。
Example 11 In the method of Example 9, an aqueous rhodium nitrate solution was used in place of chloroplatinic acid.

実施例12゜ 硝酸ビスマス水溶液とモリブデン酸アンモニア水溶:α
を酸化物換算で50g、50g秤量し、硝酸ビスマス水
溶液中にモリブデン酸アンモニウムアンモニア水溶液を
投入し、中和反応を行なった。(最終pH=7.0)以
下実施例2と同様にして触媒を得た。
Example 12゜ Bismuth nitrate aqueous solution and ammonia molybdate aqueous solution: α
50 g and 50 g in terms of oxide were weighed out, and an aqueous ammonium molybdate ammonia solution was added to an aqueous bismuth nitrate solution to perform a neutralization reaction. (Final pH=7.0) A catalyst was obtained in the same manner as in Example 2.

実施例13゜ 実施例2の方法において硝酸アルミニウムに替えて硝酸
亜鉛を用いた。
Example 13 - Zinc nitrate was used in place of aluminum nitrate in the method of Example 2.

実施例14゜ 実施例2の方法において硝酸アルミニウムに替えて塩化
スズ(II)を用いた。
Example 14 In the method of Example 2, tin(II) chloride was used in place of aluminum nitrate.

実施例15゜ 実施例1の方法において硝酸アルミニウムに替えて硝酸
鉄を用いた。
Example 15 In the method of Example 1, iron nitrate was used instead of aluminum nitrate.

実施例16゜ 実施例2の方法において塩化金酸水溶液に替えてNaを
含有する塩化金酸水(Auとして33g/見、Naとし
て3g/α)を用いた。
Example 16 In the method of Example 2, a chloroauric acid aqueous solution containing Na (33 g/in terms of Au, 3 g/α as Na) was used in place of the chloroauric acid aqueous solution.

実施例17゜ 実施例4によって得た触媒なN2−N2(1:1)の還
元性ガスで400°C1時間処理した。
Example 17 The catalyst obtained in Example 4 was treated with a reducing gas of N2-N2 (1:1) at 400°C for 1 hour.

(1)ガス組成 No      200ppm 02      2 % N20    1O% Co2   200ppm N2      バランス (2)  SV    1000 (3)反応温度  300.400.500°C試験結
果を第1表に示した。
(1) Gas composition No. 200ppm 02 2% N20 1O% Co2 200ppm N2 Balance (2) SV 1000 (3) Reaction temperature 300.400.500°C The test results are shown in Table 1.

Claims (1)

【特許請求の範囲】 窒素酸化物を含有するガスをCOの共存下で接触して、
窒素酸化物を分解除去する触媒において (a)アルカリ金属及びもしくはアルカリ土類金属酸化
物と (b)A1_2O_3、SiO_2、ZrO_2、Fe
_2O_3、TiO_2、WO_3、MoO_3、Sn
O_2、Bi_2O_3、ZnOから選択される1種以
上の金属酸化物と (c)Ru、Rh、Pd、Ag、Pt、Auから選択さ
れる1種以上の金属もしくは、金属酸化物とからなるこ
とを特徴とする窒素酸化物分解触媒
[Claims] Contacting a gas containing nitrogen oxides in the coexistence of CO,
In a catalyst that decomposes and removes nitrogen oxides, (a) an alkali metal and/or alkaline earth metal oxide and (b) A1_2O_3, SiO_2, ZrO_2, Fe
_2O_3, TiO_2, WO_3, MoO_3, Sn
Consisting of one or more metal oxides selected from O_2, Bi_2O_3, and ZnO and (c) one or more metals or metal oxides selected from Ru, Rh, Pd, Ag, Pt, and Au. Features of nitrogen oxide decomposition catalyst
JP63277694A 1988-10-05 1988-11-02 Nitrogen oxide removal catalyst Expired - Fee Related JP2689147B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP63277694A JP2689147B2 (en) 1988-11-02 1988-11-02 Nitrogen oxide removal catalyst
EP89202496A EP0362960A3 (en) 1988-10-05 1989-10-03 Use of a catalyst composition for denitrization and denitrizing catalysts
US07/417,422 US5128305A (en) 1988-10-05 1989-10-05 Catalyst for denitrization
US07/518,560 US5049364A (en) 1988-10-05 1990-06-06 Methods for denitrization

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63277694A JP2689147B2 (en) 1988-11-02 1988-11-02 Nitrogen oxide removal catalyst

Publications (2)

Publication Number Publication Date
JPH02122830A true JPH02122830A (en) 1990-05-10
JP2689147B2 JP2689147B2 (en) 1997-12-10

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Country Link
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0796187A (en) * 1993-09-28 1995-04-11 Agency Of Ind Science & Technol Catalyst for removal of nox and method for removing nox
JP2005161109A (en) * 2003-11-28 2005-06-23 Mitsubishi Heavy Ind Ltd Exhaust gas treatment catalyst and its producing method
JP2007237134A (en) * 2006-03-13 2007-09-20 Hitachi Ltd Exhaust gas purification method
US20160038921A1 (en) * 2007-02-08 2016-02-11 Daihatsu Motor Co., Ltd. Catalyst composition

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4921379A (en) * 1972-06-20 1974-02-25

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4921379A (en) * 1972-06-20 1974-02-25

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0796187A (en) * 1993-09-28 1995-04-11 Agency Of Ind Science & Technol Catalyst for removal of nox and method for removing nox
JP2005161109A (en) * 2003-11-28 2005-06-23 Mitsubishi Heavy Ind Ltd Exhaust gas treatment catalyst and its producing method
JP2007237134A (en) * 2006-03-13 2007-09-20 Hitachi Ltd Exhaust gas purification method
US20160038921A1 (en) * 2007-02-08 2016-02-11 Daihatsu Motor Co., Ltd. Catalyst composition

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