JPS6030909A - Method of cleaning exhaust gas from gas burner - Google Patents

Method of cleaning exhaust gas from gas burner

Info

Publication number
JPS6030909A
JPS6030909A JP58139381A JP13938183A JPS6030909A JP S6030909 A JPS6030909 A JP S6030909A JP 58139381 A JP58139381 A JP 58139381A JP 13938183 A JP13938183 A JP 13938183A JP S6030909 A JPS6030909 A JP S6030909A
Authority
JP
Japan
Prior art keywords
catalyst
burner
gas
mixture
exhaust gas
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
JP58139381A
Other languages
Japanese (ja)
Other versions
JPH044483B2 (en
Inventor
Satoshi Sekido
聰 関戸
Koichi Tachibana
立花 弘一
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.)
Panasonic Holdings Corp
Original Assignee
Matsushita Electric Industrial Co Ltd
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 Matsushita Electric Industrial Co Ltd filed Critical Matsushita Electric Industrial Co Ltd
Priority to JP58139381A priority Critical patent/JPS6030909A/en
Publication of JPS6030909A publication Critical patent/JPS6030909A/en
Publication of JPH044483B2 publication Critical patent/JPH044483B2/ja
Granted legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23CMETHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN  A CARRIER GAS OR AIR 
    • F23C13/00Apparatus in which combustion takes place in the presence of catalytic material

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Combustion & Propulsion (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Gas Burners (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Incineration Of Waste (AREA)
  • Catalysts (AREA)

Abstract

PURPOSE:To reduce production of noxious component such as NOX, CO contained in exhaust gas from a Bunsen type burner and a Schwank type burner, by using a catalyst formed by a perovskite type composite oxide. CONSTITUTION:A mixture ratio of the fuel to a primary air is brought to less than an equivalent, i.e., a fuel excess state to form a fuel excess range 7 in flame. A net 2, in which catalyst powder, represented by a general formula of Sr(1+x)12La(1-x)12Co1-xMaxO2, wherein Me is a metal selected from Fe, Mn, V, and Ti, and 0<x<1, is mixed with MgO, being a carrier, and magnesia mixture to firmly adhere the mixture to the surface, is located above a burner 1. The catalyst is formed by a relatively cheap element, but has a catalyst power equal to that of a precious metal and high resistance to heat. Besides, it is stable even in reducing gas, and furthermore, if basic oxide forms a carrier, catalyst activity if further improved.

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、ガスバーナの排ガス中に含まれるイj害成分
(NOX 、Go等)を減少させる方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for reducing harmful components (NOX, Go, etc.) contained in exhaust gas from a gas burner.

[従来例の描成と問題点] 従来から都市ガスおよびプロパンガス燃焼バーナとして
混合気バーナ、特にブンゼン型バーナーおよびシュバン
ク型バーナが用いられている。
[Description of conventional examples and problems] Mixture burners, particularly Bunsen type burners and Schwank type burners, have been used as city gas and propane gas combustion burners.

ブンゼン型バーナでは、予め当量混合の60〜70%の
空気を混入したガスを人気中で燃焼するが、都市ガス(
ガスの種類13A−1)を燃オ′31とした場合に排ガ
ス中には約120ppmのNOX <このうち約20%
がN02)、約9001)mのCO1約3oppmのア
ルデヒド類が含まれている。
Bunsen-type burners burn gas that has been mixed with 60 to 70% air in advance, but city gas (
When the type of gas 13A-1) is combustible gas, the exhaust gas contains approximately 120 ppm of NOX <approximately 20% of this amount.
contains about 3 oppm of aldehydes.

また、シュバンク型バーナでは、当m1lP合の90%
以上の空気を混合したガスを約33メツシユの金網を通
して燃焼するが、都市ガス(ガスの種類13A−1)を
燃料とした揚台に排ガス中に約10pDmのNOX <
このうち約5ppmがN02)、約50ppmのCO1
約45ppmのアルデヒド類が含まれている。
In addition, in the Schwunk type burner, 90% of the current m1lP
The gas mixed with the above air is combusted through a wire mesh of about 33 mesh, and about 10 pDm of NOx is produced in the exhaust gas on a platform using city gas (gas type 13A-1) as fuel.
Of this, approximately 5ppm is N02), and approximately 50ppm is CO1.
Contains about 45 ppm of aldehydes.

シュバンク型の場合はNOX、COをブンゼン型より少
なくできるが、栴造がやや複雑でガス量の調節幅(カロ
リー調節幅)が狭い点が異なっている。
In the case of the Schwunk type, NOX and CO can be reduced compared to the Bunsen type, but the difference is that the Shubunk type is slightly more complicated and the gas amount adjustment range (calorie adjustment range) is narrower.

最近、燃焼器の排ガスJP制が厳しくなり、有害ガスを
消失する触媒も多く研究され又いる。触媒としては大別
すると2種類のものが用いられている。その一つは白金
やパラジウムのような貴金属をA9203のような担体
に担持したものである。
Recently, the JP regulations for exhaust gases from combustors have become stricter, and many studies have been conducted on catalysts that eliminate harmful gases. Broadly speaking, two types of catalysts are used. One of them is one in which a noble metal such as platinum or palladium is supported on a carrier such as A9203.

いま一つは、マンガン、銅、コバル)−、ニッケルなど
の酸化物を用いたものである。後者は価格的に安価であ
るが、NOXの消失には効果がない。
Another method uses oxides such as manganese, copper, cobal, and nickel. Although the latter is inexpensive, it is not effective in eliminating NOx.

前者では、燃料と酸素の比が当量に近い所ではNOxの
消失にも効果があるが、高温にさらされると触媒金属の
焼結が進んで活性が失われ、また、価格的に高いという
欠点も有していた。
The former is effective in eliminating NOx when the ratio of fuel and oxygen is close to equivalent, but when exposed to high temperatures, sintering of the catalyst metal progresses and activity is lost, and the disadvantage is that it is expensive. It also had

(但し、MeはFe 、Mn 、V、Tiの中から選ば
れた金属、Oくχ〈1)の一般式で表わされる触媒が比
較的安価な元素で構成されながら、肖金属に匹敵する触
媒能を有し、耐熱性に富み、しかも、還元性ガス中でも
安定であること、また塩基性酸化物を担体とすると触媒
活性が更に向上することを見出し、これについて既に特
許出願済である(特願昭57−196480>。
(However, Me is a metal selected from Fe, Mn, V, and Ti, and the catalyst is represented by the general formula of It has been discovered that it has a high heat resistance, is stable even in reducing gases, and that the catalytic activity is further improved when a basic oxide is used as a carrier. Gansho 57-196480>.

[発明の目的] 本発明は、上記発明の触媒体を用いてジン1ン型および
シュバンク型バーナの排ガスを効果的に浄化する安価な
方法を提供することを目的としている。
[Object of the Invention] An object of the present invention is to provide an inexpensive method for effectively purifying the exhaust gas of a single-type burner and a Schwank type burner using the catalyst body of the above-mentioned invention.

[発明の構成コ 本発明は、混合気バーナにおいて、燃料に対りる一次空
気の混合比を当量以下すなわち燃料過剰の状態として炎
中に燃料過剰領域を形成し、この燃料過剰領域内に、一
般式 SrユLaユCO□−2M1xe3 (但し、M
eはFe 、Mn 、V、Tiの中から選ばれた金属、
Q<z<1)で表わされる触媒粉を担体であるMoOと
マグネシアセメント混合物と混合して表面に固着せしめ
た網を配置ηることを特徴とする。
[Structure of the Invention] The present invention forms a fuel excess area in the flame by setting the mixture ratio of primary air to fuel to an equivalent amount or less, that is, in a state of excess fuel, in a mixture burner, and in this excess fuel area, General formula SryuLayuCO□-2M1xe3 (However, M
e is a metal selected from Fe, Mn, V, and Ti;
It is characterized by disposing a net in which a catalyst powder represented by Q<z<1) is mixed with a carrier MoO and a magnesia cement mixture and fixed to the surface.

上記一般式で表わされる触媒は、還元性ガスの酸化と酸
化性ガスの分解還元を同時に行なう能力を持ったペロブ
スカイト型複合酸化物からなるものであり、各成分元素
の比を上記一般式のように定めたどぎに触媒活性が最も
高くなるものである。
The catalyst represented by the above general formula is made of a perovskite-type composite oxide that has the ability to simultaneously oxidize reducing gases and decompose and reduce oxidizing gases, and the ratio of each component element is determined as shown in the above general formula. The catalytic activity is highest at the point determined by .

この触媒は担体としてMoOを用いると更に活性が向上
し、本発明ではこれらに更にマグネシアセメン1〜を混
合して網の表面に固着せしめ、この触媒付網を炎の燃料
過剰領域内に配置して排ガスを浄化する。
The activity of this catalyst is further improved when MoO is used as a carrier, and in the present invention, magnesia cement 1 to 1 is further mixed with these and fixed on the surface of the net, and this catalyst-equipped net is placed in the fuel-excess region of the flame. to purify exhaust gas.

上記一般式で゛表わされる触媒は、所定の組成になるに
うに各成分元素の酸化物あるいは炭酸塩、酢酸塩などの
塩を混合し、焼成して得られる。
The catalyst represented by the above general formula is obtained by mixing oxides or salts such as carbonates and acetates of each component element to obtain a predetermined composition and calcining the mixture.

以下、本発明を添付図面に示した望ましい実施例に基づ
いて説明する。
Hereinafter, the present invention will be described based on preferred embodiments shown in the accompanying drawings.

第1a図および第1b図は本発明をブンゼン型バーナに
適用した場合の実施例である。第2a図おJ:び第2b
図は本発明をシュバンク型バーナに適用した場合の実施
例である。両者の違いは、ブンゼン型の場合には炎がガ
スの放出口から長く形成されるので、触媒のついた網を
燃料過剰領域ぐある内炎部にその内炎°周の内側に沿っ
て配置ツるのに対し、シュバンク型の場合には炎が金網
から一様に短かく形成されるので、触媒のついた絹を内
炎部の内側に沿ってガス放出網に平行に配置する点であ
る。各図において1はバーナ本体、2は触媒のついた網
、3はシュバンク型バーナのカス放出金網(約33メツ
シ1)である。4は燃r8+ガス入口、4−は混合気入
口、5は一次空気孔、6はブンゼン型バーナガス放出孔
、7は内炎部(燃料過剰領域)、8は外炎部である。
FIGS. 1a and 1b show an embodiment in which the present invention is applied to a Bunsen type burner. Figure 2a and J: and 2b
The figure shows an embodiment in which the present invention is applied to a Schwunk type burner. The difference between the two is that in the case of the Bunsen type, a long flame is formed from the gas outlet, so a net with a catalyst is placed along the inner flame circumference in the inner flame area where there is excess fuel. In contrast, in the case of the Schbank type, the flame is uniformly short and formed from the wire mesh, so the silk with the catalyst is placed along the inside of the inner flame part parallel to the gas release mesh. be. In each figure, 1 is the burner main body, 2 is a mesh with a catalyst, and 3 is a wire mesh (approximately 33 mesh 1) for discharging the waste of the Schwunk type burner. 4 is a fuel r8+ gas inlet, 4- is a mixture inlet, 5 is a primary air hole, 6 is a Bunsen type burner gas discharge hole, 7 is an inner flame part (fuel excess area), and 8 is an outer flame part.

[実験例の説明] 友11上 3000kca l / 11のブンゼン型バーナでガ
ス全開とし、当量空気量に対して、1次空気の割合(P
a)を40〜85%の範囲で変えて燃焼を行なった。燃
焼状態の最もよいpa=85%において、3.5.1゜
メツシュのステンレス性の金網に、5r1−aO,90
,1 COo、2 Fe0.803 、MU Ozマグネシア
セメントをそれぞれ固形分mm比で(3:3:1の割合
で練合した触媒を200μmの厚さに塗布し、固着せし
めた金網を内炎周に沿って内側に第1図のように配置し
た。触媒網の頂部とガス放出孔との距離は、3メツシユ
そ35mm、5メツシユで50 m +n、1oメツシ
ユで7011mとなった。この状態でPaを変え、排ガ
ス中のNOXとCOの′a度の変化を測定した。
[Explanation of experimental example] A 3000 kcal/11 Bunsen burner on the Tomo 11 was set to full gas, and the ratio of primary air to the equivalent air amount (P
Combustion was carried out by varying a) in the range of 40 to 85%. At the best combustion condition, pa = 85%, 5r1-aO, 90
, 1 COo, 2 Fe0.803 and MU Oz magnesia cement were mixed with a solid content mm ratio of 3:3:1, and then the catalyst was applied to a thickness of 200 μm, and a fixed wire mesh was placed around the inner flame periphery. The distance between the top of the catalyst network and the gas release holes was 35 mm for 3 meshes, 50 m + n for 5 meshes, and 7011 m for 1 o mesh.In this state, By changing Pa, changes in NOX and CO in the exhaust gas were measured.

それらの測定値をそれぞれ第3図および第4図に示した
。図中、実線は3000kcal/ hの場合で、Aは
触媒金網なし、Bは3メツシユ、Cは5メツシユ、Dは
10メツシコの金網に触媒をつけたものである。点線D
′はDについて1000kca l / hの燃焼の伯
を示したものである。
The measured values are shown in FIGS. 3 and 4, respectively. In the figure, the solid line indicates the case of 3000 kcal/h, where A is without catalyst wire mesh, B is with 3 meshes, C is with 5 meshes, and D is with catalyst attached to 10 meshes of wire mesh. Dotted line D
' indicates the combustion ratio of 1000 kcal/h for D.

いずれの触媒金網を用いても有害ガスはpa−60〜7
0%の所で最少となる。金網のメツシュが細かい程浄化
能が優れていることが認められる。
No matter which catalyst wire mesh is used, harmful gases will reach pa-60 to 7.
It is minimum at 0%. It is recognized that the finer the wire mesh, the better the purification ability.

実験例2 実″皺例1の8!I!奴網をPa=95%のシュバンク
型バーナに第2図のように取(d l−J T燃焼を行
なった。
Experimental Example 2 The 8!I! net from Example 1 was placed in a Schwunk type burner with Pa = 95% as shown in Fig. 2 (d l-J T combustion was performed).

シュバンク型バーナ固有の33メツシユの金網からの触
媒網の距離は1〜2mmが適当であった。
The appropriate distance of the catalyst mesh from the 33-mesh wire mesh unique to the Schwunk type burner was 1 to 2 mm.

NOxとCOの測定伯はそれぞれ表1のようになった。The measurement values for NOx and CO were as shown in Table 1.

表1 シュバンク型バーナにおいても触媒の浄化能はメツシュ
が細かい程優れている。
Table 1 Even in Schwunk type burners, the finer the mesh, the better the purification ability of the catalyst.

実験例3 10メツシユの金網に実験例1のように触媒を塗布した
ものと、アルミナセメントに1%の割合で白金黒を加え
塗布したものを作り、3000kca l / h 。
Experimental Example 3 A wire mesh of 10 meshes coated with a catalyst as in Experimental Example 1, and alumina cement coated with 1% platinum black were made, and the yield was 3000 kcal/h.

Pa=65%のブンゼンバーナに実験例1と同様に取付
けて燃焼実験を行ない排ガス成分の変化を測定した。
It was attached to a Bunsen burner with Pa=65% in the same manner as in Experimental Example 1, and a combustion experiment was conducted to measure changes in exhaust gas components.

第5図に測定値を示した。図中、E 、E−は本発明の
もの、F、F−は白金黒を用いたものである。実線E 
、FはNOX、点線E−、F−はCOの測定値を示して
いる。
Figure 5 shows the measured values. In the figure, E and E- are those of the present invention, and F and F- are those using platinum black. Solid line E
, F indicates NOX, and dotted lines E- and F- indicate measured values of CO.

本発明の触媒は初期は白金黒に較べて浄化能がやや劣る
が、経時劣化が少なく、長期間にわたって高い浄化能を
維持した。
Initially, the catalyst of the present invention had a slightly inferior purification ability compared to platinum black, but it showed little deterioration over time and maintained high purification ability over a long period of time.

[発明の効果] 以上のように本発明は安価な拐料である触媒体を耐熱性
に優れたステンレスのような金網や無機酸化物繊維から
なる網に温度をかけるような高価な手段でなく同者担持
させ、これを内炎周内部に配誼ツ゛ることにより、燃焼
を阻害することなく、白金など高価な触媒を用いるもの
より長期にわたって高い浄化能を発揮し、特に安価で熱
量制御幅の広いブンゼン型バーナにおいてもシュバンク
型バーナ程度の有害ガス排出用に抑えることができるな
どの効果を有する。
[Effects of the Invention] As described above, the present invention does not require expensive means such as applying heat to a catalyst body, which is an inexpensive filtrate, to a highly heat-resistant wire mesh such as stainless steel or a mesh made of inorganic oxide fibers. By supporting the catalyst and distributing it inside the inner flame periphery, it does not inhibit combustion and exhibits higher purification ability over a longer period of time than those using expensive catalysts such as platinum. Even in a Bunsen-type burner with a wide width, the exhaust gas can be suppressed to the same level as a Schwunk-type burner.

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

第1a図は本発明のブンゼン型バーナにお(プる実施例
を触媒金網の部分を一部切り欠いて示寸斜視図、第1b
図は同実施例の燃焼状態を示す断面図、 第2a図は本発明のシュバンク型バーナにおりる実施例
を触媒金網の部分を一部切り欠いて示り平面図、第2b
図は同実施例の燃焼状態を示り断面図、 第3図は本発明実験例1のNOx浄化の程度を表わす図
、 第4図は本発明実験例1のCOγ道化の程度を表わす図
、 第5図は実験例3の従来例との比較にお【プる触媒寿命
を表わす図である。 1・・・バーナ本体 2・・・触媒網 3・・・シュバ
ンク型バーナガス放出網 4・・・燃料ガス入口 4′
・・・混合気入口 6・・・ブンゼン型バーナガス放出
LJ 7・・・内炎部 8・・・外炎部 特許出願人 松下電器産業株式会社 第1a図 簿ib図 i2a図 第2b図 纂a図 第4図
Fig. 1a is a perspective view showing a Bunsen-type burner according to the present invention (with part of the catalyst wire mesh cut away);
Figure 2a is a cross-sectional view showing the combustion state of the same embodiment, Figure 2a is a plan view showing an embodiment of the Schwunk type burner of the present invention with the catalyst wire mesh partially cut away, and Figure 2b is a plan view showing the combustion state of the same embodiment.
Figure 3 is a cross-sectional view showing the combustion state of the same example. Figure 3 is a diagram showing the degree of NOx purification in Experimental Example 1 of the present invention. Figure 4 is a diagram showing the degree of CO gamma deterioration in Experimental Example 1 of the present invention. , FIG. 5 is a diagram showing the catalyst life in comparison with the conventional example of Experimental Example 3. 1...Burner body 2...Catalyst network 3...Schbank type burner gas discharge network 4...Fuel gas inlet 4'
...Mixture mixture inlet 6...Bunsen type burner gas discharge LJ 7...Inner flame section 8...Outer flame section Patent applicant Matsushita Electric Industrial Co., Ltd. Figure 1a Book ib Figure i2a Figure 2b Figure 2a Collection a Figure 4

Claims (4)

【特許請求の範囲】[Claims] (1) 混合気バーナにおいて、燃料に対する一次空気
の混合比を当量以下(燃料過剰)とし、炎のMezO3
(但し、MeはFe 、Mn 、V、Tiの中から選ば
れた金属、Oくχ〈1)で表わされる触媒粉を担体であ
るMIJ○とマグネシアセメント混合物と混合して表面
に固着せしめた網を配置することを特徴とするガスバー
ナの排ガス浄化方法。
(1) In the mixture burner, the mixture ratio of primary air to fuel is equal to or less than the equivalent amount (fuel excess), and the MezO3 of the flame
(Me is a metal selected from Fe, Mn, V, and Ti, and catalyst powder represented by A method for purifying exhaust gas from a gas burner, characterized by arranging a net.
(2) 前記混合気バーナがブンゼン型バーナであり、
前記網を内炎部内にその内炎部の内側に沿って配置する
特許請求の範囲第(1)項に記載のガスバーナの排ガス
浄化方法。
(2) the mixture burner is a Bunsen type burner;
The exhaust gas purifying method for a gas burner according to claim (1), wherein the net is arranged inside the inner flame section along the inside of the inner flame section.
(3)前記混合気バーナがシュバンク型バーナであり、
前記網を内炎部内にその内炎部の内側に沿ってガス放出
網に平行に配置する特許請求の範囲第(1)項に記載の
ガスバーナの排ガス浄化方法。
(3) the mixture burner is a Schwunk type burner;
The exhaust gas purifying method for a gas burner according to claim 1, wherein the net is arranged inside the inner flame section along the inside of the inner flame section and parallel to the gas release net.
(4) 前記網が金網または無機酸化物41維からなる
特許請求の範囲第(1)項乃至第(3)項のいずれかに
記載のガスバーナの排ガス浄化方法。
(4) The method for purifying exhaust gas from a gas burner according to any one of claims (1) to (3), wherein the mesh is made of a wire mesh or an inorganic oxide 41 fiber.
JP58139381A 1983-08-01 1983-08-01 Method of cleaning exhaust gas from gas burner Granted JPS6030909A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58139381A JPS6030909A (en) 1983-08-01 1983-08-01 Method of cleaning exhaust gas from gas burner

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58139381A JPS6030909A (en) 1983-08-01 1983-08-01 Method of cleaning exhaust gas from gas burner

Publications (2)

Publication Number Publication Date
JPS6030909A true JPS6030909A (en) 1985-02-16
JPH044483B2 JPH044483B2 (en) 1992-01-28

Family

ID=15243989

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58139381A Granted JPS6030909A (en) 1983-08-01 1983-08-01 Method of cleaning exhaust gas from gas burner

Country Status (1)

Country Link
JP (1) JPS6030909A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63158130A (en) * 1986-12-23 1988-07-01 Tech Res Assoc Conduct Inorg Compo Catalyst for purifying exhaust gas
EP0777085A3 (en) * 1995-12-01 1998-08-05 Carrier Corporation Catalytic insert for NOx reduction
EP2045522A1 (en) * 2007-10-05 2009-04-08 Riello S.p.A. Hybrid combustion boiler

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63158130A (en) * 1986-12-23 1988-07-01 Tech Res Assoc Conduct Inorg Compo Catalyst for purifying exhaust gas
EP0777085A3 (en) * 1995-12-01 1998-08-05 Carrier Corporation Catalytic insert for NOx reduction
EP2045522A1 (en) * 2007-10-05 2009-04-08 Riello S.p.A. Hybrid combustion boiler

Also Published As

Publication number Publication date
JPH044483B2 (en) 1992-01-28

Similar Documents

Publication Publication Date Title
KR100234887B1 (en) Catalyst structure having integral heat exchange
US5149508A (en) Parallel path catalytic converter
EP0401646A1 (en) Metallic core member for catalytic converter and catalytic converter containing same
EP1741480A2 (en) Apparatus for removing particulate matter
US20090148357A1 (en) Apparatus and catalyst for purifying exhaust gas
JP2007275738A (en) Oxidation catalyst for purifying exhaust gas
JPS6030909A (en) Method of cleaning exhaust gas from gas burner
JPS63267804A (en) Oxidizing catalyst for high temperature service
CN103209927B (en) Layered mixed oxide, oxidation catalyst and diesel particulate filter
JPS6118434A (en) Catalytic body for purifying exhaust gas
WO2022097330A1 (en) Exhaust gas purifying catalyst and exhaust gas treatment apparatus
JP4226143B2 (en) Catalytic combustion apparatus and combustion control method thereof
JPH02157043A (en) Exhaust gas cleanup catalyst
JPH06129613A (en) Catalyst combustion device
JPS61283349A (en) Catalyst for purifying exhaust gas
JPH0347144B2 (en)
JPS63267805A (en) Oxidizing catalyst for high temperature service
JPH01317540A (en) Oxidizing catalyst
JPH07136513A (en) Waste gas treating oxidation catalyst
JPH0377642A (en) Catalyst for purification of exhaust gas
JPH0949609A (en) Burning method for combustible gas
JPH05306808A (en) Catalyic combustion device
JPH01270943A (en) Perovskite oxidation catalyst
JPS63267803A (en) Oxidizing catalyst for high temperature service
JPH04187240A (en) Catalyst for purification of exhaust gas