JPH044483B2 - - Google Patents

Info

Publication number
JPH044483B2
JPH044483B2 JP58139381A JP13938183A JPH044483B2 JP H044483 B2 JPH044483 B2 JP H044483B2 JP 58139381 A JP58139381 A JP 58139381A JP 13938183 A JP13938183 A JP 13938183A JP H044483 B2 JPH044483 B2 JP H044483B2
Authority
JP
Japan
Prior art keywords
burner
fuel
gas
mesh
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.)
Expired - Lifetime
Application number
JP58139381A
Other languages
Japanese (ja)
Other versions
JPS6030909A (en
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 filed Critical
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)
  • Incineration Of Waste (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Gas Burners (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

[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有
害成分(NOx、CO等)を減少させる方法に関す
る。 [従来例の構成と問題点] 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お
よびシユバンク型バーナが用いられている。 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大気中で燃焼するが、
都市ガス(ガスの種類13A−1)を燃料とした場
合に排ガス中には約120ppmのNOx(このうち約
20%がNO2)、約90ppmのCO、約30ppmのアルデ
ヒド類が含まれている。 また、シユバンク型バーナでは、当量混合の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)を燃料とした場合に排ガス中に約
10ppmのNOx(このうち約5ppmがNO2)、約
50ppmのCO、約45ppmのアルデヒド類が含まれ
ている。 シユバンク型の場合はNOx、COをブンゼン型
より少なくできるが、構造がやや複雑でガス量の
調節幅(カロリー調節幅)が狭い点が異なつてい
る。 最近、燃焼器の排ガス規制が厳しくなり、有害
ガスを消失する触媒も多く研究されている。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Al2O3のような担体に担持したものである。い
ま一つは、マンガン、銅、コバルト、ニツケルな
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。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。 本発明者らは、
[Industrial Application Field] The present invention relates to a method for reducing harmful components (NOx, CO, etc.) contained in exhaust gas from a gas burner. [Configuration and Problems of Conventional Examples] Conventionally, mixture burners, particularly Bunsen type burners and Schubank type burners, have been used as city gas and propane gas combustion burners. In a Bunsen type burner, 60 to 70
% of air is burned in the atmosphere,
When city gas (gas type 13A-1) is used as fuel, the exhaust gas contains approximately 120 ppm of NOx (of which approximately
It contains 20% NO 2 ), about 90 ppm CO, and about 30 ppm aldehydes. In addition, in the bank type burner, 90
Gas mixed with more than 30% air is burned through a wire mesh of about 33 mesh, but city gas (type of gas)
13A-1) is used as fuel, approximately
10ppm NOx (of which about 5ppm is NO 2 ), approx.
Contains 50ppm CO and about 45ppm aldehydes. The Schubank type can reduce NOx and CO than the Bunsen type, but the difference is that the structure is somewhat more complex and the gas amount adjustment range (calorie adjustment range) is narrower. Recently, combustor exhaust gas regulations have become stricter, and much research has been conducted into catalysts that eliminate harmful gases. Broadly speaking, two types of catalysts are used. One is one in which a noble metal such as platinum or palladium is supported on a support such as Al 2 O 3 . The other type uses oxides such as manganese, copper, cobalt, and nickel. Although the latter is inexpensive, it is not effective in eliminating NOx. In the former case, where the ratio of fuel and oxygen is close to equivalence,
Although it is effective in eliminating NOx, it also has the disadvantage that when exposed to high temperatures, the catalytic metal sinters and loses its activity, and it is also expensive. The inventors

【式】(但し、Meは Fe、Mn、V、Tiの中から選ばれた金属、0<x
<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、貴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)。 [発明の目的] 本発明は、上記発明の触媒体を用いてブンゼン
型およびシユ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。 [発明の構成] 本発明は、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
[Formula] (Me is a metal selected from Fe, Mn, V, Ti, 0<x
Although the catalyst represented by the general formula of It was discovered that the catalytic activity was further improved when an oxide was used as a carrier, and a patent application has already been filed for this (patent application filed in 1983).
196480). [Object of the Invention] An object of the present invention is to provide an inexpensive method for effectively purifying exhaust gas from Bunsen type and Schubank type burners using the catalyst body of the above invention. [Structure of the Invention] The present invention forms an excess fuel region 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 an air-fuel mixture burner, and in this excess fuel region, the general formula

【式】(但し、Meは Fe、Mn、V、Tiの中から選ばれた金属、0<x
<1)で表わされる触媒粉を担体であるMgO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。 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
を持つ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
定めたときに触媒活性が最も高くなるものであ
る。この触媒は担体としてMgO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
アセメント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。 上記一般式で表わされる触媒は、所定の組成に
なるよ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。 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。 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
および第2b図は本発明をシユバンク型バーナに
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で
ある内炎部にその内炎周の内側に沿つて配置する
のに対し、シユ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、触媒のついた網を
内炎周の内側に沿つ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はシユバンク型のバーナのガ
ス放出金網(約33メツシユ)である。4は燃料ガ
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。 [実験例の説明] 実験例 1 3000kcal/h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(Pa)
を40〜85%の範囲で変えて燃焼を行なつた。燃焼
状態の最もよいPa=65%において、3、5、10
メツシユのステンレス性の金網に、Sr0.9La0.1
Co0.2Fe0.8O3、MgO、マグネシアセメントをそれ
ぞれ固形分重量比で6:3:1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
網を内炎周に沿つて内側に第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
ツシユで35mm、5メツシユで50mm、10メツシユで
70mmとなつた。この状態でPaを変え、排ガス中
のNOxとCOの濃度の変化を測定した。 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メツシユの金網に触媒をつけたもの
である。点線D′はDについて1000kcal/hの燃
焼の値を示したものである。 いずれの触媒金網を用いても有害ガスはPa=
60〜70%の所で最少となる。金網のメツシユが細
かい程浄化能が優れていることが認められる。 実験例 2 実験例1の触媒網をPa=95%のシユバンク型
バーナに第2図のように取付けて燃焼を行なつ
た。シユ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が適当であつた。 NOxとCOの測定値はそれぞれ表1のようにな
つた。
[Formula] (Me is a metal selected from Fe, Mn, V, Ti, 0<x
It is characterized by disposing a net in which the catalyst powder represented by <1) is mixed with a mixture of MgO and magnesia cement as a carrier and fixed to the surface. 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 when the The activity of this catalyst is further improved when MgO is used as a carrier, and in the present invention, magnesia cement 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 emit exhaust gas. Purify. The catalyst represented by the above general formula is made of oxides or carbonates of each component element so as to have a predetermined composition.
It is obtained by mixing a salt such as acetate and firing the mixture. Hereinafter, the present invention will be described based on preferred embodiments shown in the accompanying drawings. FIGS. 1a and 1b show an embodiment in which the present invention is applied to a Bunsen type burner. FIGS. 2a and 2b show an embodiment in which the present invention is applied to a bunk 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 inside of the periphery of the inner flame in the inner flame area, which is the fuel-excess area. On the other hand, in the case of the Shubank type, the flame is uniformly formed from a short wire mesh, so the mesh with the catalyst is arranged parallel to the gas release mesh along the inner side of the inner flame periphery. In each figure, 1 is the burner body, 2 is a mesh with a catalyst, and 3 is a gas release wire mesh (approximately 33 meshes) of the bank-type burner. 4 is the fuel gas inlet, 4' is the mixture inlet, 5 is the primary air hole, 6
1 is a Bunsen-type burner gas discharge hole, 7 is an inner flame part (fuel excess area), and 8 is an outer flame part. [Explanation of experimental examples] Experimental example 1 A 3000 kcal/h Bunsen burner with gas fully opened, ratio of primary air to equivalent air amount (Pa)
The combustion was carried out by varying the amount in the range of 40% to 85%. At the best combustion condition Pa=65%, 3, 5, 10
Sr 0.9 La 0.1 on mesh stainless steel wire mesh
A catalyst prepared by mixing Co 0.2 Fe 0.8 O 3 , MgO, and magnesia cement in a solid weight ratio of 6:3:1 was applied to a thickness of 200 μm, and a fixed wire mesh was placed along the inner flame periphery. It was placed inside as shown in Figure 1. The distance between the top of the catalyst network and the gas release hole is 35 mm for 3 meshes, 50 mm for 5 meshes, and 50 mm for 10 meshes.
It became 70mm. Under this condition, Pa was changed and changes in the concentrations of NOx and CO in the exhaust gas were measured. The measured values are shown in FIGS. 3 and 4, respectively. In the figure, the solid line is for 3000kcal/h,
A has no catalyst wire mesh, B has 3 meshes, C has 5 meshes, and D has a 10 mesh wire mesh with a catalyst attached. The dotted line D' shows the combustion value of 1000 kcal/h for D. No matter which catalyst wire mesh is used, the harmful gas will be Pa=
It reaches its minimum at 60-70%. It is recognized that the finer the mesh of the wire mesh, the better the purification ability. Experimental Example 2 The catalyst network of Experimental Example 1 was attached to a Shubank type burner with Pa=95% as shown in Fig. 2, and combustion was carried out. The appropriate distance of the catalyst mesh from the 33-mesh wire mesh unique to the bank type burner was 1 to 2 mm. The measured values of NOx and CO were as shown in Table 1.

【表】 シユバンク型バーナにおいても触媒の浄化能は
メツシユが細かい程優れている。 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、3000kcal/
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。 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。 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、長期間にわたつ
て高い浄化能を維持した。 [発明の効果] 以上のように本発明は安価な材料である触媒体
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
な手段でなく固着担持させ、これを内炎周内部に
配置することにより、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
つ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ユバンク型
バーナ程度の有害ガス排出量に抑えることができ
るなどの効果を有する。
[Table] Even in bank-type burners, the finer the mesh, the better the purification ability of the catalyst. Experimental Example 3 A 10-mesh wire mesh was coated with a catalyst as in Experimental Example 1, and alumina cement was coated with platinum black at a rate of 1%, and 3000 kcal/
A combustion experiment was conducted by attaching it to a Bunsen burner with h and Pa = 65% in the same manner as in Experimental Example 1, and changes in exhaust gas components were measured. 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.
The solid lines E and F show the measured values of NOx, and the dotted lines E' and F' show the measured values of CO. Although the catalyst of the present invention initially had a slightly inferior purification ability compared to platinum black, it showed little deterioration over time and maintained high purification ability over a long period of time. [Effects of the Invention] As described above, the present invention allows the catalyst body, which is an inexpensive material, to be fixed to a highly heat-resistant wire mesh such as stainless steel or a mesh made of inorganic oxide fibers without using expensive means such as applying heat. By supporting it and placing it inside the inner flame periphery, combustion is not inhibited.
It exhibits higher purification ability over a long period of time than those that use expensive catalysts such as platinum, and has the advantage of being able to suppress harmful gas emissions to the same level as a Schubank burner, even with a Bunsen burner that is inexpensive and has a wide range of heat control. has.

【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ける
実施例を触媒金網の部分を一部切り欠いて示す斜
視図、第1b図は同実施例の燃焼状態を示す断面
図、第2a図は本発明のシユバンク型バーナにお
ける実施例を触媒金網の部分を一部切り欠いて示
す平面図、第2b図は同実施例の燃焼状態を示す
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CO
浄化の程度を表わす図、第5図は実験例3の従来
例との比較における触媒寿命を表わす図である。 1……バーナ本体、2……触媒網、3……シユ
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
ナガス放出口、7……内炎部、8……外炎部。
Fig. 1a is a perspective view showing an embodiment of the Bunsen type burner of the present invention with a part of the catalyst wire cut away, Fig. 1b is a cross-sectional view showing the combustion state of the embodiment, and Fig. 2a is a Fig. 2b is a cross-sectional view showing the combustion state of the embodiment, and Fig. 3 is the degree of NOx purification in Experimental Example 1 of the present invention. Figure 4 shows the CO of Experimental Example 1 of the present invention.
FIG. 5 is a diagram showing the degree of purification, and 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...Shubunk type burner gas discharge network, 4...Fuel gas inlet, 4'...Mixture inlet, 6...Bunsen type burner gas discharge port, 7...Inner flame Part, 8... External inflammation part.

Claims (1)

【特許請求の範囲】 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、炎の燃
料過剰領域内に、一般式
【式】(但し、Meは Fe、Mn、V、Tiの中から選ばれた金属、0<x
<1)で表わされる触媒粉を担体であるMgO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。 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周の内側に沿つ
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。 3 前記混合気バーナがシユバンク型バーナであ
り、前記網を内炎部内にその内炎周の内側に沿つ
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。 4 前記網が金網または無機酸化物繊維からなる
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。
[Claims] 1. In the air-fuel mixture burner, the mixture ratio of primary air to fuel is equal to or less than equivalent (fuel excess), and within the fuel excess region of the flame, the general formula [formula] (where Me is Fe, Mn, V, metal selected from Ti, 0<x
A method for purifying exhaust gas from a gas burner, characterized by arranging a net in which the catalyst powder represented by <1) is mixed with a carrier of MgO and a magnesia cement mixture and fixed to the surface. 2. The exhaust gas purification method for a gas burner according to claim 1, wherein the air-fuel mixture burner is a Bunsen type burner, and the net is disposed inside the inner flame portion along the inner side of the periphery of the inner flame. 3. Exhaust gas purification of a gas burner according to claim 1, wherein the air-fuel mixture burner is a sybank type burner, and the mesh is disposed inside the inner flame section along the inner side of the inner flame periphery and parallel to the gas discharge network. Method. 4. The exhaust gas purification method for 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 fiber.
JP58139381A 1983-08-01 1983-08-01 Gas burner exhaust gas purification method Granted JPS6030909A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58139381A JPS6030909A (en) 1983-08-01 1983-08-01 Gas burner exhaust gas purification method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58139381A JPS6030909A (en) 1983-08-01 1983-08-01 Gas burner exhaust gas purification method

Publications (2)

Publication Number Publication Date
JPS6030909A JPS6030909A (en) 1985-02-16
JPH044483B2 true 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 Gas burner exhaust gas purification method

Country Status (1)

Country Link
JP (1) JPS6030909A (en)

Families Citing this family (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
US5746194A (en) * 1995-12-01 1998-05-05 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
JPS6030909A (en) 1985-02-16

Similar Documents

Publication Publication Date Title
US5814285A (en) Poisoning-preventive layer-possessing support, poisoning-resistant catalyst, exhaust gas converter device, and poisoning-preventive gasoline composition
JPH06506139A (en) Catalyst structure (II) with combined heat exchange
US6774080B2 (en) Gas treatment device comprising SMSI material and methods for making and using the same
JP3364492B2 (en) Multi-stage combustion method for fuel mixtures
JPS61249541A (en) oxidation catalyst
US20090148357A1 (en) Apparatus and catalyst for purifying exhaust gas
JPH044483B2 (en)
EP1898153A1 (en) Gas burner for cooking appliances
JPS6380848A (en) Catalytic system for combustion of high pressure methane based fuel and combustion method using the same
JPS63267804A (en) Oxidizing catalyst for high temperature service
JPH0438454B2 (en)
JPH07136513A (en) Waste gas treating oxidation catalyst
JPH0464736B2 (en)
JP3244938B2 (en) Combustible gas combustion method
JPH02191548A (en) Catalyst for purification of exhaust gas
JPS63267805A (en) Oxidizing catalyst for high temperature service
KR950003413B1 (en) Method of preparing catalyst for complete combustion of stove
JPH06129613A (en) Catalytic combustion device
US7772149B2 (en) Exhaust gas purification apparatus for an internal combustion engine and a catalyst for purifying exhaust gas
JPS63232852A (en) Catalyst for gas turbine burner and its production
JPS634852A (en) Catalyst for combustion
JPH0377644A (en) Catalyst for purification of exhaust gas
JPH0377642A (en) Catalyst for purification of exhaust gas
JPS5922657A (en) Catalyst
JPS61242640A (en) Oxidation catalyst