JP3507538B2 - Exhaust gas purification catalyst and purification method - Google Patents

Exhaust gas purification catalyst and purification method

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Publication number
JP3507538B2
JP3507538B2 JP01283694A JP1283694A JP3507538B2 JP 3507538 B2 JP3507538 B2 JP 3507538B2 JP 01283694 A JP01283694 A JP 01283694A JP 1283694 A JP1283694 A JP 1283694A JP 3507538 B2 JP3507538 B2 JP 3507538B2
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JP
Japan
Prior art keywords
catalyst
exhaust gas
platinum
purification
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.)
Expired - Fee Related
Application number
JP01283694A
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Japanese (ja)
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JPH07213914A (en
Inventor
邦彦 小西
泰良 加藤
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Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
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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、排ガス化触媒およ
浄化方法に関し、さらに詳しくは排ガス中の窒素酸化
物(NOx)、一酸化炭素(CO)およびアンモニア
(NH3 )の浄化に好適な排ガス化触媒および浄化
方法に関する。
BACKGROUND OF THE INVENTION This invention relates to medium and purifying methods catalyst purification of exhaust gas, more particularly nitrogen oxides in the exhaust gas (NOx), the purification of carbon monoxide (CO) and ammonia (NH 3) suitable for waste gas purification of catalysts and purification
Regarding the method .

【0002】[0002]

【従来の技術】ボイラから排出される燃焼排ガス中の窒
素酸化物(NOx)は、光化学スモッグや酸性雨の原因
物質であるため、NOxを除去する方法として、触媒を
用いて排ガス中に添加したアンモニア(NH3 )で選択
的に還元する接触還元法が広く採用されている。上記触
媒としては、酸化チタンをベースにした各種の脱硝触
媒、例えば、触媒成分をハニカム状や球状に成形した触
媒、セラミックスハニカムや金属基板上に触媒成分をコ
ーティングして触媒使用量を低減した触媒等が実用化さ
れている(特開昭50−128681号公報、特開昭5
3−28148号公報、特開平2−83086号公
報)。
2. Description of the Related Art Nitrogen oxide (NOx) in combustion exhaust gas discharged from a boiler is a causative substance of photochemical smog and acid rain. Therefore, as a method of removing NOx, it was added to exhaust gas using a catalyst. A catalytic reduction method of selectively reducing with ammonia (NH 3 ) is widely adopted. As the catalyst, various denitration catalysts based on titanium oxide, for example, a catalyst in which the catalyst component is formed into a honeycomb shape or a spherical shape, or a catalyst whose catalyst usage amount is reduced by coating the catalyst component on a ceramic honeycomb or a metal substrate Have been put into practical use (Japanese Patent Laid-Open No. 50-128681, Japanese Laid-Open Patent Publication No.
3-28148, JP-A-2-83086).

【0003】一方、最近では、排ガス中のNOxだけで
なく、同時に排ガス中のCOの除去や還元剤として注入
したNH3 の未反応NH3 流出量の低減が求められてお
り、これらの成分を同時に浄化する触媒や浄化方法等の
開発が進められている。例えば特開平5−329334
号公報には、NOxとCOを除去し、かつ未反応アンモ
ニアの流出量の低減を図ることができる触媒、具体的に
は白金を担持したシリカまたはモルデナイトと酸化チタ
ン系脱硝触媒成分とを組合わせた触媒が開示されてい
る。
On the other hand, in recent years, not only NOx in the exhaust gas, and the reduction of unreacted NH 3 outflow of the NH 3 injected is obtained as removing or reducing agents CO in the exhaust gas simultaneously these components At the same time, the development of catalysts and purification methods for purifying is ongoing. For example, Japanese Patent Laid-Open No. 5-329334
Japanese Patent Laid-Open Publication No. 2003-242242 discloses a catalyst capable of removing NOx and CO and reducing the outflow amount of unreacted ammonia, specifically, silica or mordenite carrying platinum and a titanium oxide-based denitration catalyst component in combination. Other catalysts are disclosed.

【0004】[0004]

【発明が解決しようとする課題】しかし、上記触媒で
は、NOxとNH3 の除去反応が下記式(1)および
(2)式の反応により行われ、触媒表面層でNH3 が白
金触媒と接触して酸化されてNOを生成するため、この
生成したNOが残留NH3 と反応する確率が少なくな
り、結果的に排ガス中のNO濃度が低くならず、脱硝性
能が悪くなるという問題があった。 NO+NH3 +3/4 O2 → N2 +3/2 H2 O (1) NH3 +5/4 O2 → NO+3/2 H2 O (2)
However, in the above catalyst, the removal reaction of NOx and NH 3 is carried out by the reaction of the following formulas (1) and (2), and NH 3 comes into contact with the platinum catalyst in the catalyst surface layer. As a result, the generated NO is less likely to react with the residual NH 3 because it is oxidized to generate NO, and as a result, the NO concentration in the exhaust gas is not lowered and the denitration performance is deteriorated. . NO + NH 3 + 3/4 O 2 → N 2 + 3/2 H 2 O (1) NH 3 + 5/4 O 2 → NO + 3/2 H 2 O (2)

【0005】すなわち、排ガス中のNOxは、還元剤と
してのNH3 の存在下で触媒中の酸化チタン系脱硝触媒
成分により(1)式の反応でN2 とH2 Oとなる。一
方、(1)式の反応に使用されなかった未反応のNH3
は、触媒内の白金触媒の存在下で(2)式によりNOに
酸化される。生成したNOは、白金触媒粒子に隣接する
脱硝触媒粒子および残存するNH3 と接触して(1)式
の反応によりN2 とH2 Oとなり、その結果、未反応N
3 の系外への流出量が低減されることとなる。しか
し、白金触媒と脱硝触媒成分を混合したものを成形また
は基板上にコーティングした上記従来の触媒では、該触
媒表面において、NH3 が触媒表面上の白金触媒と接触
してNOを生成するため、このNOが残留するNH3
接触して上記(1)の反応をする機会が少なくなり、脱
硝率が低下すると考えられる。
That is, NOx in the exhaust gas becomes N 2 and H 2 O in the reaction of the formula (1) by the titanium oxide type denitration catalyst component in the catalyst in the presence of NH 3 as a reducing agent. On the other hand, unreacted NH 3 not used in the reaction of the formula (1)
Is oxidized to NO by the formula (2) in the presence of a platinum catalyst in the catalyst. The generated NO is brought into contact with the denitration catalyst particles adjacent to the platinum catalyst particles and the remaining NH 3 to become N 2 and H 2 O by the reaction of the formula (1), and as a result, unreacted N 3
The amount of H 3 flowing out of the system will be reduced. However, in the above-mentioned conventional catalyst in which a mixture of a platinum catalyst and a denitration catalyst component is molded or coated on a substrate, NH 3 comes into contact with the platinum catalyst on the catalyst surface to generate NO on the catalyst surface, It is considered that this NO reduces the chances of contacting the remaining NH 3 with the reaction of the above (1) to reduce the denitration rate.

【0006】 本発明の目的は、上記従来技術の問題点
を解決し、少ない触媒使用量で、NOxとCOの除去お
よび未反応NH3 の流出量の低減を効率よく行うことが
できる排ガス化触媒および浄化方法を提供すること
にある。
An object of the present invention shows the above-mentioned solution to the problems of the prior art, a small amount of catalyst used, Kiyoshi exhaust gas to a reduction in the outflow of removal and unreacted NH 3 in NOx and CO can be efficiently and to provide a reduction catalytic and purification method.

【0007】[0007]

【課題を解決するための手段】本願で特許請求される発
明は以下のとおりである。 (1)金属基板上に、該金属基板側から白金成分層と脱
硝触媒成分層を順担持させたことを特徴とする窒素酸
化物、一酸化炭素およびアンモニアを含有する排ガス
化触媒。 (2)(1)記載の脱硝触媒成分が、酸化チタンと酸化
モリブデンと酸化バナジウムの混合物、酸化チタンと酸
化タングステンと酸化バナジウムの混合物または酸化チ
タンと酸化バナジウムの混合物であることを特徴とする
窒素酸化物、一酸化炭素およびアンモニアを含有する
ガス化触媒。 (3)窒素酸化物、一酸化炭素およびアンモニアを含有
する排ガスを触媒の存在下に浄化する排ガス浄化方法で
あって、該触媒として、(1)または(2)に記載の浄
化触媒を用いることを特徴とする排ガス浄化方法。
The inventions claimed in this application are as follows. (1) on a metal substrate, a nitrogen acid which is characterized in that the platinum component layer and the denitration catalyst component layer is sequential carried from the metal substrate
Products, waste gas <br/> purification of catalysts containing carbon monoxide and ammonia. (2) The denitration catalyst component according to (1) is characterized in that it is a mixture of titanium oxide, molybdenum oxide and vanadium oxide, a mixture of titanium oxide, tungsten oxide and vanadium oxide or a mixture of titanium oxide and vanadium oxide.
Nitrogen oxides, purification of catalytic material discharge <br/> gas containing carbon monoxide and ammonia. (3) Contains nitrogen oxide, carbon monoxide and ammonia
Exhaust gas purification method that purifies the exhaust gas in the presence of a catalyst
Therefore, as the catalyst, the purification according to (1) or (2)
A method for purifying exhaust gas, which comprises using a oxidization catalyst.

【0008】図1は、本発明の排ガス浄化用触媒の一例
を示す断面模式図である。図において、排ガス浄化用触
媒1は、金属基板2上に白金粒子層3と脱硝触媒粒子層
4を順に有する。排ガス中のNOxは、まず、触媒表面
の脱硝触媒粒子層4と接触し、NH3 と反応してN2
2 Oとなる。この脱硝触媒粒子層4には白金粒子が存
在しないため、NH3 が酸化されてNOになることはな
い。NOxと反応しなかった未反応のNH3 は、脱硝触
媒粒子層4の内部に拡散し、白金粒子層3と接触してN
Oに酸化される。発生したNOは、白金粒子に隣接する
脱硝触媒粒子と接触して残存するNH3 と反応し、N2
とH2 Oとなる。一方、排ガス中のCOは、触媒内を容
易に拡散する性質があるため、速やかに白金酸化触媒成
分3と接触してCO2 に酸化される。
FIG. 1 is a schematic sectional view showing an example of an exhaust gas purifying catalyst of the present invention. In the figure, the exhaust gas-purifying catalyst 1 has a platinum particle layer 3 and a denitration catalyst particle layer 4 in this order on a metal substrate 2. NOx in the exhaust gas first contacts the denitration catalyst particle layer 4 on the catalyst surface and reacts with NH 3 to become N 2 and H 2 O. Since the denitration catalyst particle layer 4 has no platinum particles, NH 3 is not oxidized to NO. The unreacted NH 3 that has not reacted with NOx diffuses inside the denitration catalyst particle layer 4 and comes into contact with the platinum particle layer 3 to generate N.
Oxidized to O. The generated NO reacts with the remaining NH 3 in contact with the denitration catalyst particles adjacent to the platinum particles, and N 2
And H 2 O. On the other hand, since CO in the exhaust gas has a property of easily diffusing in the catalyst, it is quickly contacted with the platinum oxidation catalyst component 3 and is oxidized to CO 2 .

【0009】このように本発明の排ガス浄化用触媒で
は、従来の触媒のように白金粒子が触媒表面に出ておら
ず、触媒表面層でNH3 がNOに酸化されることがない
ため、NOがそのまま系外に排出されることはなく高い
脱硝率を得ることができ、しかも排ガス中のCOをも容
易に酸化でき、かつ未反応NH3 の流出量も大幅に低減
することができる。また本発明の排ガス浄化用触媒は、
金属基板上に各触媒成分をそれぞれ薄くコーティングす
ることにより得られるため、触媒使用量の低減が図れ
る。例えば、エキスパンドメタルにコーティングした場
合、従来のエキスパンドメタルの目開きを触媒で充填し
た形状の板状触媒と較べ、触媒使用量が1/10以下に
でき、経済的に優れたものとなる。
As described above, in the exhaust gas purifying catalyst of the present invention, unlike the conventional catalyst, the platinum particles do not appear on the catalyst surface, and NH 3 is not oxidized to NO in the catalyst surface layer. However, it is possible to obtain a high denitration rate without being discharged to the outside of the system as it is, and moreover, CO in the exhaust gas can be easily oxidized and the outflow amount of unreacted NH 3 can be greatly reduced. Further, the exhaust gas purifying catalyst of the present invention,
Since it can be obtained by thinly coating each catalyst component on a metal substrate, the amount of catalyst used can be reduced. For example, when the expanded metal is coated, the amount of the catalyst used can be reduced to 1/10 or less, which is economically superior to the conventional plate-shaped catalyst in which the openings of the expanded metal are filled with the catalyst.

【0010】本発明に用いられる金属基板としては特に
制限はなく、ステンレス鋼、軟鋼等いずれでも使用する
ことができ、またその形状も平板、網状、エキスパンド
メタル等いずれでも使用可能である。該金属表面をアル
ミニウム等で金属溶射処理して粗面を形成させた金属基
板は、金属表面と触媒との接触が強化され、また触媒表
面積が増加し、活性が向上するため好ましい。本発明に
おける白金成分層は、例えば白金の塩化物、硝酸塩等の
可溶性塩類またはアミン錯体の形で溶解した水溶液中に
金属基板を浸漬し、またはこの水溶液を金属基板に塗布
し、該金属表面に白金をイオン交換させて担持し、乾燥
することにより得られる。
The metal substrate used in the present invention is not particularly limited, and any of stainless steel, mild steel and the like can be used, and the shape thereof can also be any of flat plate, net, expanded metal and the like. A metal substrate having a rough surface formed by subjecting the metal surface to a metal spray treatment with aluminum or the like is preferable because the contact between the metal surface and the catalyst is strengthened, the catalyst surface area is increased, and the activity is improved. The platinum component layer in the present invention is, for example, a chloride of platinum, a metal substrate is immersed in an aqueous solution dissolved in the form of a soluble salt such as nitrate or an amine complex, or the aqueous solution is applied to the metal substrate, and the metal surface is coated on the metal surface. It is obtained by carrying out ion exchange of platinum, supporting it, and drying.

【0011】本発明における脱硝触媒成分には、触媒成
分の活性、分散性および剥離強度等の点から、酸化チタ
ンと酸化モリブデンと酸化バナジウムの混合物、酸化チ
タンと酸化タングステンと酸化バナジウムの混合物また
は酸化チタンと酸化バナジウムの混合物が用いられる。
脱硝触媒成分層は、例えば、上記酸化物の混合粉末を水
に懸濁させてスラリー化し、上記白金成分層を有する金
属基板上に塗布して数十μmの厚さに担持させ、その
後、公知の方法で乾燥、焼成することにより得られる。
The denitration catalyst component in the present invention is a mixture of titanium oxide, molybdenum oxide and vanadium oxide, a mixture of titanium oxide, tungsten oxide and vanadium oxide or an oxide, from the viewpoints of activity, dispersibility and peel strength of the catalyst component. A mixture of titanium and vanadium oxide is used.
For the denitration catalyst component layer, for example, a mixed powder of the above oxide is suspended in water to form a slurry, which is applied onto a metal substrate having the above platinum component layer to support it to a thickness of several tens of μm, and then a known method is used. It is obtained by drying and baking by the method of.

【0012】[0012]

【実施例】以下、本発明を実施例により詳しく説明す
る。 実施例1 厚さ0.2mmのSUS304製エキスパンドメタル1m
2 を、濃度20mg/lの塩化白金酸水溶液中に浸漬し、
エキスパンドメタル表面に白金をイオン交換させて担持
した。この基板を水洗後乾燥させて触媒基板とした。酸
化チタン30重量%を含むメタチタン酸50kgに、モリ
ブデン酸アンモニウム3.81kgおよびメタバナジン酸
アンモニウム1.04kgを加え、ニーダで加熱混練し、
水分35重量%のペーストを得た。このペーストを押出
造粒機で造粒後、乾燥し、550℃で2時間焼成した。
得られた顆粒をハンマーハルで100メッシュパス90
%以上に粉砕した。この粉末5.4kgに水4.6kgを加
えて懸濁させて脱硝触媒のスラリを得た。このスラリ
に、前記白金を担持した基板を浸漬し、余剰のスラリを
除去した後、乾燥し、500℃で2時間焼成して担持量
が150g/m2 の触媒を得た。
EXAMPLES The present invention will be described in detail below with reference to examples. Example 1 1 m of SUS304 expanded metal with a thickness of 0.2 mm
2 is immersed in an aqueous solution of chloroplatinic acid having a concentration of 20 mg / l,
Platinum was ion-exchanged and supported on the surface of the expanded metal. This substrate was washed with water and dried to give a catalyst substrate. To 50 kg of metatitanic acid containing 30% by weight of titanium oxide, 3.81 kg of ammonium molybdate and 1.04 kg of ammonium metavanadate are added and kneaded by heating with a kneader,
A paste having a water content of 35% by weight was obtained. This paste was granulated by an extrusion granulator, dried, and calcined at 550 ° C for 2 hours.
100 granules 90 of the obtained granules with a hammer hull
Crushed to over%. Water (4.6 kg) was added to and suspended in 5.4 kg of this powder to obtain a slurry of a denitration catalyst. The platinum-supported substrate was immersed in this slurry to remove excess slurry, dried and calcined at 500 ° C. for 2 hours to obtain a catalyst having a supported amount of 150 g / m 2 .

【0013】実施例2 実施例1において、塩化白金酸水溶液をエキスパンドメ
タルに塗布し、乾燥後、500℃で2時間焼成してエキ
スパンドメタルに白金を担持させた以外は、実施例1と
同様の方法で触媒を調製した。 実施例3 実施例2において、塩化白金酸水溶液の代わりにジニト
ロジアンミン白金水溶液を使用した以外は、実施例2と
同様の方法で触媒を調製した。 実施例4 実施例2において、SUS304製エキスパンドメタル
の代わりにアルミニウム溶射を50g/m2 施したSU
S304製エキスパンドメタルを使用した以外は、実施
例2と同様の方法で触媒を調製した。
Example 2 The same as Example 1 except that the aqueous solution of chloroplatinic acid was applied to the expanded metal, dried and then baked at 500 ° C. for 2 hours to support platinum on the expanded metal. A catalyst was prepared by the method. Example 3 A catalyst was prepared in the same manner as in Example 2 except that an aqueous dinitrodiammine platinum solution was used instead of the chloroplatinic acid aqueous solution. Example 4 In Example 2, SU in which aluminum was sprayed at 50 g / m 2 instead of the SUS304 expanded metal
A catalyst was prepared in the same manner as in Example 2 except that the expanded metal manufactured by S304 was used.

【0014】比較例1 シリカ粉末5kgに、塩化白金酸6.64gを水8lに溶
解させた塩化白金酸水溶液を加えて加熱しながら攪拌
し、塩化白金酸を担持したシリカ粉末を得た。この塩化
白金酸担持シリカ粉末を乾燥後、500℃で2時間焼成
して白金を0.05%担持したシリカとした。この白金
を0.05%担持したシリカ粉末と、実施例1で使用し
たチタン、モリブデンおよびバナジウムの酸化物からな
る脱硝触媒の粉末を、重量比で2:98の割合で混合
し、これに水を添加し、攪拌懸濁して触媒のスラリを得
た。このスラリ中に厚さ0.2mmのSUS304製エキ
スパンドメタルを触媒基板を浸漬し、実施例1と同様に
乾燥、焼成して触媒の担持量が150g/m2 の触媒を
得た。
Comparative Example 1 To 5 kg of silica powder was added an aqueous solution of chloroplatinic acid in which 6.64 g of chloroplatinic acid was dissolved in 8 l of water, and the mixture was stirred with heating to obtain silica powder carrying chloroplatinic acid. The silica powder carrying chloroplatinic acid was dried and then calcined at 500 ° C. for 2 hours to obtain silica carrying 0.05% of platinum. The silica powder supporting 0.05% of platinum and the powder of the denitration catalyst composed of the oxides of titanium, molybdenum and vanadium used in Example 1 were mixed at a weight ratio of 2:98 and mixed with water. Was added, and the mixture was stirred and suspended to obtain a catalyst slurry. A 0.2 mm-thick SUS304 expanded metal was immersed in this slurry, and the catalyst substrate was dried and calcined in the same manner as in Example 1 to obtain a catalyst having a catalyst loading of 150 g / m 2 .

【0015】<試験例>実施例1〜4および比較例1で
得られたそれぞれの触媒を用いて排ガス処理を行い、N
Oの除去率、COの除去率およびNH3 の流出量を調べ
た。使用した排ガス成分および処理条件を表1に示し、
得られた結果を表2に示した。
<Test Example> Exhaust gas treatment was performed using each of the catalysts obtained in Examples 1 to 4 and Comparative Example 1, and N
The removal rate of O, the removal rate of CO, and the outflow amount of NH 3 were examined. The exhaust gas components and treatment conditions used are shown in Table 1,
The obtained results are shown in Table 2.

【表1】 [Table 1]

【0016】[0016]

【表2】 [Table 2]

【0017】表2から、金属基板上に白金を担持させ、
その上に脱硝触媒を薄層にコーティングした構造の触媒
(実施例1〜4)では、白金を担持したシリカと脱硝触
媒成分とを混合した触媒をコーティングしたもの(比較
例1)と同等のNH3 分解率を示し、かつ脱硝率は、単
に白金を担持したシリカと脱硝触媒成分を混合してコー
ティングした触媒に較べて格段に高い性能を示すことが
わかる。
From Table 2, platinum is supported on a metal substrate,
The catalyst having a structure in which a thin layer of the denitration catalyst is coated thereon (Examples 1 to 4) has the same NH as that of the catalyst coated with the platinum-supported silica and the denitration catalyst component (Comparative Example 1). It can be seen that the decomposition rate is 3 and the denitrification rate is much higher than that of a catalyst obtained by simply mixing platinum-supported silica and a denitration catalyst component and coating the mixture.

【0018】[0018]

【発明の効果】本発明の排ガス用浄化触媒および浄化方
によれば、触媒表層部でのNH3 のNOへの酸化反応
が起きないため、また未反応NH3 が基板表面上の白金
粒子によりNOに酸化された後、該NOが隣接する脱硝
触媒上で残留NH3 と反応してN2 とH2 Oとされるた
め、脱硝性能の低下を招くことなく、しかも未反応NH
3 の流出量を低減することができる。また排ガス中のC
Oも触媒中の白金成分によりCO2 に酸化されて除去さ
れる。従って、本発明の触媒を用いた脱硝装置は、低コ
ストで流出NH3 を抑え、しかも高脱硝率とCOの除去
を達成することができる。また触媒使用量を少なくする
ことができるため、経済性に優れる。
EFFECT OF THE INVENTION Exhaust gas purifying catalyst and purifying method of the present invention
According to the method , since the oxidation reaction of NH 3 to NO does not occur in the surface layer of the catalyst, and after the unreacted NH 3 is oxidized to NO by the platinum particles on the substrate surface, the NO is adjoined to the NOx removal catalyst. Since it reacts with the residual NH 3 to form N 2 and H 2 O above, it does not deteriorate the denitration performance, and the unreacted NH
The outflow amount of 3 can be reduced. Also, C in the exhaust gas
O is also oxidized and removed by CO 2 due to the platinum component in the catalyst. Therefore, the denitration apparatus using the catalyst of the present invention can suppress outflowing NH 3 at low cost and can achieve a high denitration rate and CO removal. It is possible to reduce the or catalytic amount, excellent economy.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の排ガス浄化用触媒の一例を示す断面模
式図。
FIG. 1 is a schematic sectional view showing an example of an exhaust gas purifying catalyst of the present invention.

【符号の説明】[Explanation of symbols]

1…排ガス浄化用触媒、2…金属基板、3…白金粒子
層、4…脱硝触媒粒子層。
1 ... Exhaust gas purifying catalyst, 2 ... Metal substrate, 3 ... Platinum particle layer, 4 ... Denitration catalyst particle layer.

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B01J 21/00 - 38/74 B01D 53/00 - 53/96 ─────────────────────────────────────────────────── ─── Continuation of the front page (58) Fields surveyed (Int.Cl. 7 , DB name) B01J 21/00-38/74 B01D 53/00-53/96

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 金属基板上に、該金属基板側から白金成
分層と脱硝触媒成分層を順担持させたことを特徴とす
窒素酸化物、一酸化炭素およびアンモニアを含有する
排ガス化触媒。
To 1. A metal substrate, <br/> containing nitrogen oxides, characterized in that the platinum component layer and the denitration catalyst component layer is sequential carried from the metal substrate, the carbon monoxide and ammonia exhaust gas for purification of catalysts.
【請求項2】 請求項1記載の脱硝触媒成分が、酸化チ
タンと酸化モリブデンと酸化バナジウムの混合物、酸化
チタンと酸化タングステンと酸化バナジウムの混合物ま
たは酸化チタンと酸化バナジウムの混合物であることを
特徴とする窒素酸化物、一酸化炭素およびアンモニアを
含有する排ガス化触媒。
2. The denitration catalyst component according to claim 1, which is a mixture of titanium oxide, molybdenum oxide and vanadium oxide, a mixture of titanium oxide, tungsten oxide and vanadium oxide or a mixture of titanium oxide and vanadium oxide. Nitrogen oxides, carbon monoxide and ammonia
Waste gas purification of catalysts containing.
【請求項3】 窒素酸化物、一酸化炭素およびアンモニ
アを含有する排ガスを触媒の存在下に浄化する排ガス浄
化方法であって、該触媒として、請求項1または請求項
2に記載の浄化触媒を用いることを特徴とする排ガス浄
化方法。
3. Nitrogen oxides, carbon monoxide and ammonia
Exhaust gas purification that purifies exhaust gas containing a in the presence of a catalyst
The method of claim 1, wherein the catalyst is used as the catalyst.
Exhaust gas purification characterized by using the purification catalyst described in 2.
Method.
JP01283694A 1994-02-04 1994-02-04 Exhaust gas purification catalyst and purification method Expired - Fee Related JP3507538B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP01283694A JP3507538B2 (en) 1994-02-04 1994-02-04 Exhaust gas purification catalyst and purification method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP01283694A JP3507538B2 (en) 1994-02-04 1994-02-04 Exhaust gas purification catalyst and purification method

Publications (2)

Publication Number Publication Date
JPH07213914A JPH07213914A (en) 1995-08-15
JP3507538B2 true JP3507538B2 (en) 2004-03-15

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ID=11816469

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Country Status (1)

Country Link
JP (1) JP3507538B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112107993B (en) * 2019-06-21 2022-08-16 中国石化工程建设有限公司 Denitration method and system for flue gas of incomplete regeneration catalytic cracking device
CN117019143A (en) * 2023-07-21 2023-11-10 中节能(山东)催化剂有限公司 Denitration, decarbonization and deamination three-effect composite catalyst and preparation method thereof

Also Published As

Publication number Publication date
JPH07213914A (en) 1995-08-15

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