Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPS5813807B2 - Nitrogen oxide reduction method - Google Patents
[go: Go Back, main page]

JPS5813807B2 - Nitrogen oxide reduction method - Google Patents

Nitrogen oxide reduction method

Info

Publication number
JPS5813807B2
JPS5813807B2 JP51107894A JP10789476A JPS5813807B2 JP S5813807 B2 JPS5813807 B2 JP S5813807B2 JP 51107894 A JP51107894 A JP 51107894A JP 10789476 A JP10789476 A JP 10789476A JP S5813807 B2 JPS5813807 B2 JP S5813807B2
Authority
JP
Japan
Prior art keywords
combustion
exhaust gas
air
gas
afterburning
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
Application number
JP51107894A
Other languages
Japanese (ja)
Other versions
JPS5333421A (en
Inventor
坂井正康
徳田君代
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP51107894A priority Critical patent/JPS5813807B2/en
Publication of JPS5333421A publication Critical patent/JPS5333421A/en
Publication of JPS5813807B2 publication Critical patent/JPS5813807B2/en
Expired legal-status Critical Current

Links

Landscapes

  • Incineration Of Waste (AREA)
  • Air Supply (AREA)
  • Chimneys And Flues (AREA)

Description

【発明の詳細な説明】 本発明は燃焼排ガス中の窒素酸化物Noxを低減させる
方法の改良に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improvement in a method for reducing nitrogen oxides Nox in combustion exhaust gas.

窒素酸化物低減燃焼法(以下、低NOx燃焼法とも呼ぶ
)としては,次の3種の方法があり,現在ではこれらの
方法を単独または組合わせて燃焼ガス中のNOxの低減
を図っている。
There are three types of nitrogen oxide reduction combustion methods (hereinafter also referred to as low NOx combustion methods), and these methods are currently being used alone or in combination to reduce NOx in combustion gas. .

(1)オーバ・ファイヤ・エア法(OFA法)第1図の
燃焼炉1において、燃料は配管3を通ってバーナ4に送
られ炉内に噴出され,燃焼用空気Aは配管2からバーナ
部2Bへ送られるA2と,燃焼ゾーンの後部2人へ送ら
れるA1とに分けられる。
(1) Over-fire air method (OFA method) In the combustion furnace 1 shown in Fig. 1, fuel is sent to the burner 4 through piping 3 and is ejected into the furnace, and combustion air A is sent from piping 2 to the burner section. It is divided into A2, which is sent to 2B, and A1, which is sent to the two people at the rear of the combustion zone.

このようにすると,主燃焼炎Cは空気不足の低温火炎と
なってNOx発生が抑えられ,未燃焼燃料は領域5で配
管2人からの空気A1により燃焼を完結させ,煙道6を
経て排出される排ガスG中のNOx量を低減させる。
In this way, the main combustion flame C becomes a low-temperature flame lacking air, suppressing NOx generation, and the unburned fuel is completely combusted in area 5 by air A1 from the two pipes, and is discharged through the flue 6. This reduces the amount of NOx in the exhaust gas G.

(2)ガス再循環法(GR法) 第2図の燃焼炉1に燃料を配管3よりバーナ4に送り,
配管2より送られる空気Aによって燃焼を行ない,燃焼
炎Cを形成するとき,煙道6を流れる排ガスGの一部G
aをバイパスW路8に設けた再循環ガスファン7によっ
て燃焼炎Cの上流となる炉底1aに吹き込む。
(2) Gas recirculation method (GR method) Fuel is sent to the combustion furnace 1 in Fig. 2 from the piping 3 to the burner 4.
When combustion is performed by the air A sent from the pipe 2 and a combustion flame C is formed, a part of the exhaust gas G flowing through the flue 6
A is blown into the furnace bottom 1a upstream of the combustion flame C by a recirculating gas fan 7 provided in the bypass W path 8.

この再循環ガスの送り込みによって火炎温度を下げNO
x発生を抑える。
By feeding this recirculated gas, the flame temperature is lowered and the NO
Suppress the occurrence of x.

(3)再循環ガス混入法(GM法) 第3図の燃焼炉1において,配管3より送られた燃料は
配管2より送られた空気Aによって炉内で燃焼するが、
ここで発生する排ガスGの一部Gaを再循環ガスファン
7によって配管2からの空気Aに混入する。
(3) Recirculating gas mixing method (GM method) In the combustion furnace 1 shown in Fig. 3, the fuel sent from the pipe 3 is combusted in the furnace by the air A sent from the pipe 2.
A part of Ga of the exhaust gas G generated here is mixed into the air A from the pipe 2 by the recirculating gas fan 7.

この再循環ガスの混入した空気Agによって燃焼する燃
焼炎Cは再循環ガスの混入しない空気Aのみによって燃
焼する場合よりも低い温度に抑えられ,これによってN
Oxの発生も抑えられる。
The combustion flame C that burns due to the air Ag mixed with this recirculated gas is suppressed to a lower temperature than when combustion is performed only with air A not mixed with the recirculated gas.
The generation of Ox can also be suppressed.

しかしながら.これらの方法で達成される燃焼ゾーンに
2けるNOxの低減レベルは限度があり将来の循環規制
を満足できるものではないので,本出願人はその改良法
として前に特願昭51−23728号としてアフタバー
ニング法を提案した。
however. The reduction level of NOx in the combustion zone 2 achieved by these methods is limited and cannot satisfy future circulation regulations, so the applicant has previously proposed an improved method as Japanese Patent Application No. 1983-23728. proposed an afterburning method.

該アフタバーナ法は下記のような方法である。The afterburner method is as follows.

(4)アフタバーナ法(特願昭51−23728号)第
4図の燃焼炉1内に燃料配管3よりバーナ4を経て送ら
れた燃料を配管2より送られた空気Aによって通常の燃
焼を行なう。
(4) Afterburner method (Japanese Patent Application No. 51-23728) The fuel sent from fuel pipe 3 through burner 4 into combustion furnace 1 shown in Fig. 4 is normally combusted by air A sent from pipe 2. .

この際生じる燃焼炎Cの排ガスGは煙道6を通って排気
されるが,この煙道6の途中にアフタバーニング用の空
気吹き込み口10およびその後流部にアフタバーナ9が
設けられており,アフタバーニング用空気Aaは配管2
aより,アフタバーナ9へ行くAa2と空気吹き込み口
10へ行<Aa1とに分けられる。
The exhaust gas G of the combustion flame C generated at this time is exhausted through the flue 6, and an afterburner 9 is provided in the middle of the flue 6 for the purpose of afterburning. Burning air Aa is pipe 2
From a, the air is divided into Aa2, which goes to the afterburner 9, and Aa1, which goes to the air blowing port 10.

アフナバーニングの際の燃料は配管3aより送られ空気
Aa2と一次燃焼を終えた後,空気Aa1を混入した排
ガスG中の酸素と2次燃焼を行なって燃焼は完結する。
The fuel for the AFNA burning is sent through the pipe 3a, and after completing primary combustion with the air Aa2, it undergoes secondary combustion with the oxygen in the exhaust gas G mixed with the air Aa1, and the combustion is completed.

このときの作用を説明すると,燃焼炉1における燃焼炎
Cは低過剰酸素燃焼をさせる程NOx発生を低く抑える
ことができるが,一般には残酸素2〜3%が限度でこれ
以下ではCO発生または発煙をみる。
To explain the effect at this time, the combustion flame C in the combustion furnace 1 can suppress NOx generation to the extent that it performs low excess oxygen combustion, but generally the residual oxygen is limited to 2 to 3%, and below this, CO generation or Look for smoke.

したがって残022〜3%の排ガスGにアフタバーニン
グ用空気の一部Aa1を予め混合させ,アフタバーナ9
の燃焼ガスEを空気比の小さい(理論比より小)燃焼と
することができる状態をつくる。
Therefore, part of the afterburning air Aa1 is mixed in advance with the remaining 022 to 3% exhaust gas G, and the afterburning air 9
A condition is created in which the combustion gas E can be combusted with a small air ratio (lower than the theoretical ratio).

理論空気量以下の空気比0.05〜0.6の燃焼ガスと
なるようアフタバーナ9の燃料と空気A・a2は調整さ
れている。
The fuel and air A/a2 in the afterburner 9 are adjusted so that the combustion gas has an air ratio of 0.05 to 0.6, which is less than the theoretical air amount.

なお空気比0.05以下ではCO発生または発煙が起り
,0.6以上では十分なNOx低減効果が得られない。
Note that when the air ratio is less than 0.05, CO generation or smoke occurs, and when it is more than 0.6, a sufficient NOx reduction effect cannot be obtained.

排ガス中の窒素酸化物NOxを低減させる方法には,上
記(1)〜(4)等の方法があるが,この中で特に脱硝
率が良いとされるアフタバーナ法の場合でも,第5図に
示す実験例のようにガス温度が200〜600℃の範囲
では,脱硝率は90%を越えるが,人体に有害なCO及
びHCを発生し、更に800〜1050℃の範囲ではC
O及びHCの発生はないが脱硝率は50%程度である。
There are methods (1) to (4) mentioned above to reduce nitrogen oxide NOx in exhaust gas, but even in the afterburner method, which is said to have a particularly good denitrification rate, the method shown in Figure 5 is As shown in the experimental example shown, when the gas temperature is in the range of 200 to 600°C, the denitrification rate exceeds 90%, but CO and HC, which are harmful to the human body, are generated, and in the range of 800 to 1050°C, carbon
Although there is no generation of O and HC, the denitrification rate is about 50%.

第5図で横軸はアフタバーニング域でのガス温度,縦軸
は脱硝率およびCO,HCの量を表わすそこで本発明者
等は上記アフタバーニング法よりも更に効果的なNOx
低減法を見出すべく鋭意研究の結果アフタバーニング法
にGR法を組み合わせ,或は更にGM法を組み合わせる
ことによって,NOxを更に低減させうることを見出し
,その知見に基いて本発明を完成するに至った。
In Fig. 5, the horizontal axis represents the gas temperature in the afterburning region, and the vertical axis represents the denitrification rate and the amount of CO and HC.
As a result of intensive research to find ways to reduce NOx, we discovered that it is possible to further reduce NOx by combining the afterburning method with the GR method, or further with the GM method, and based on this knowledge we have completed the present invention. Ta.

すなわち、本発明は (1)火炉の燃焼系で生成した窒素酸化物を含む温度6
50〜1100℃の燃焼排ガス中で,燃料を空気比0.
05〜0.60の空気量の下でアフタバーニングを行な
い、アフタバーニングされた排ガスの一部を上記火炉の
燃焼系へ再循環路を介して再循環させることを特徴とす
る窒素酸化物低減法。
That is, the present invention has the following advantages: (1) Temperature 6 containing nitrogen oxides generated in the combustion system of a furnace
In combustion exhaust gas at a temperature of 50 to 1100°C, fuel is mixed at an air ratio of 0.
A method for reducing nitrogen oxides, characterized in that afterburning is performed under an air amount of 0.05 to 0.60, and a part of the afterburned exhaust gas is recirculated to the combustion system of the furnace via a recirculation path. .

(2)火炉の燃焼系で生成した窒素酸化物を含む温度6
50〜1100℃の燃焼排ガス中で,燃料を空気比0.
05〜0.60の空気量の下でアフタバーニングを行な
い,アフタバーニングされた排ガスの一部を上記火炉の
燃焼系の再循環路を介して再循環させる方法において再
循環路で温度が200〜600℃に下った排ガス中で空
気比0.05〜0.60の空気量の下で更にアフタバー
ニングを行なうことを特徴とする窒素酸化物低減法。
(2) Temperature 6 containing nitrogen oxides generated in the combustion system of the furnace
In combustion exhaust gas at a temperature of 50 to 1100°C, fuel is mixed at an air ratio of 0.
In a method in which afterburning is performed under an air amount of 0.05 to 0.60, and a part of the afterburned exhaust gas is recirculated through the recirculation path of the combustion system of the furnace, the temperature in the recirculation path is 200 to 0.60. A method for reducing nitrogen oxides, characterized in that afterburning is further performed in the exhaust gas at a temperature of 600° C. under an air amount having an air ratio of 0.05 to 0.60.

に関するものである。It is related to.

本発明は,ガス燃料,液体燃料及び固体燃料を使用する
如何なるボイラ及び一般工業用加熱炉にも適用すること
ができる。
The present invention can be applied to any boiler or general industrial heating furnace that uses gas fuel, liquid fuel, or solid fuel.

以下、本発明の窒素酸化物低減法を第6図を参照しなが
ら、詳述する。
Hereinafter, the method for reducing nitrogen oxides of the present invention will be explained in detail with reference to FIG.

第6図において,1は燃焼炉,2はバーナ,3は煙道、
4は第1次アフタバーナであって,このアフタバーナ4
は特願昭51−23728号明細書に詳述されているよ
うに上記煙道3の途中に設けられている。
In Figure 6, 1 is a combustion furnace, 2 is a burner, 3 is a flue,
4 is a primary afterburner, and this afterburner 4
is provided in the middle of the flue 3 as detailed in Japanese Patent Application No. 51-23728.

5は再循環ダクトで上記煙道3の上記アフタバーナ4の
後流から分岐した流路で再循環ガス混入法(GM法)と
ガス再循環法(GR法)とをそれぞれ構成できるように
下流において分岐し,ダクト6,7が形成されている。
Reference numeral 5 denotes a recirculation duct, which is a flow path branching from the downstream side of the afterburner 4 in the flue 3, and is installed downstream so as to configure a recirculation gas mixing method (GM method) and a gas recirculation method (GR method), respectively. It branches to form ducts 6 and 7.

8は再循環ガスファンであって,上記再循環ダクト5の
途中に設けられて上記煙道3の排ガスを吸引し上記ダク
ト6,7に送風する。
A recirculation gas fan 8 is provided in the middle of the recirculation duct 5 to suck in exhaust gas from the flue 3 and blow it into the ducts 6 and 7.

9は第2次アフタバーナであって,上記再循環ダクト5
内のダクト6,7の上流に設けられている。
9 is a secondary afterburner, which is connected to the recirculation duct 5.
It is provided upstream of the ducts 6 and 7 inside.

なお図中のマルで囲んだ記号の意味は次の通りである。The meanings of the symbols enclosed in circles in the figure are as follows.

Go=主燃焼排ガスのガス量 GA:主燃焼ガス用アフタバーナのガス量GR:再循環
ガス量 GB:再循環ガス用アフタバーナのガス量No:主燃焼
排ガスのNOx濃度 NY:燃焼室出口NOx濃度 Nx:大気放出排ガスNOx濃度 NR:再循環ガスのアフタバーニング後のNOx濃度 また A:空 気 F:燃 料 G:排ガス C:火 炎 である。
Go = Gas amount of main combustion exhaust gas GA: Gas amount of afterburner for main combustion gas GR: Recirculation gas amount GB: Gas amount of afterburner for recirculation gas No.: NOx concentration of main combustion exhaust gas NY: Combustion chamber outlet NOx concentration Nx : NOx concentration of exhaust gas released into the atmosphere NR: NOx concentration after afterburning of recirculated gas A: Air F: Fuel G: Exhaust gas C: Flame.

バーナ2で燃焼された火炎Cの排ガスは,一般に過剰酸
素を2〜3%含んでいる。
The exhaust gas from the flame C burned in the burner 2 generally contains 2 to 3% excess oxygen.

この燃焼排ガス中のNOxを煙道3に設けた第1次アフ
タバーナ4によってアフタバーニングを行ないNoXを
低減させる。
The NOx in this combustion exhaust gas is subjected to afterburning by a primary afterburner 4 provided in the flue 3 to reduce Nox.

このアフタバーナ4の空気比は0,05〜0.60であ
る。
The air ratio of this afterburner 4 is 0.05 to 0.60.

アフタバーニングされた排ガスの一部は.再循環ダクト
5を通って,燃焼炉1内へダクト6,7を経て再循環さ
れる。
Some of the afterburned exhaust gas. It is recirculated through the recirculation duct 5 into the combustion furnace 1 via ducts 6 and 7.

排ガスの残部は煙道3を通って大気へ放出される。The remainder of the exhaust gas is discharged to the atmosphere through the flue 3.

再循環された排ガスは,温度が600℃以下となり再循
環ダクト5に設けられた第2次アフタバーナ9によって
,低温燃焼されNOxが更に低減される。
The temperature of the recirculated exhaust gas becomes 600° C. or lower, and the secondary afterburner 9 provided in the recirculation duct 5 burns the exhaust gas at a low temperature to further reduce NOx.

この時の燃焼条件も第1次アフタバーニング条件と同じ
で空気比0.05〜0.60の空気量の下で行なわれる
The combustion conditions at this time are the same as the first afterburning conditions, and the combustion is carried out under an air amount with an air ratio of 0.05 to 0.60.

ここで,第1次アフタバーナ4及び第2次アフタバーナ
9のNOx低減割合をη4及びη,とすると, であり, NYは次式により求まる。
Here, if the NOx reduction ratios of the primary afterburner 4 and the secondary afterburner 9 are η4 and η, then NY is determined by the following equation.

?なる。? Become.

−゜上記,η4,η,に前述した第5図 に示した実験結果より得られた数値を代入し,NOx低
減割合Nx/Noを求めたものを第1表に示す。
-° Table 1 shows the NOx reduction ratio Nx/No obtained by substituting the numerical values obtained from the experimental results shown in FIG. 5 mentioned above into η4 and η.

この結果第1表の種々のNOx低減対策から判かるよう
に,従来のアフタバーニング法単独■では、NOx低減
効果は50%程度であったが、再循環法◎を併用するこ
とによって33.3%迄低減可能である。
As can be seen from the various NOx reduction measures in Table 1, the conventional afterburning method (■) alone had a NOx reduction effect of about 50%, but when combined with the recirculation method (◎), the NOx reduction effect was 33.3%. %.

更に再循環排ガスを第2次アフタバーナ9でアフタバー
ニングする方法■により,25.6%あるいは17.2
%迄NOxの低減が可能となった。
Furthermore, by the method (2) of afterburning the recirculated exhaust gas with the secondary afterburner 9, the reduction rate is 25.6% or 17.2%.
It has become possible to reduce NOx up to %.

従って,従来もつともNOx低減効果が良いとされてい
たアフタバーニング法単独よりも更に%〜%NOxを低
減できる。
Therefore, it is possible to reduce NOx by % to % more than the afterburning method alone, which has conventionally been considered to have a good NOx reduction effect.

なお、アフタバーナで使用される燃料は一般的に炭化水
素系燃料であり,ダクト6,7へのガス量及び配分は任
意であって,例えばダクト6に100%循環させ、ダク
ト7をO%にしてもよく,又その逆であってもよい。
The fuel used in the afterburner is generally a hydrocarbon fuel, and the gas amount and distribution to the ducts 6 and 7 are arbitrary. or vice versa.

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

第1図〜第4図は従来の窒素酸化物低減法の説明図,第
5図は,アフタバーニング域でのガス温度と脱硝率.C
O,HC量の関係を表わす図表、第6図は本発明方法の
説明図である。
Figures 1 to 4 are explanatory diagrams of conventional nitrogen oxide reduction methods, and Figure 5 shows gas temperature and denitrification rate in the afterburning region. C
FIG. 6, a chart showing the relationship between O and HC amounts, is an explanatory diagram of the method of the present invention.

Claims (1)

【特許請求の範囲】 1 火炉の燃焼系で生成した窒素酸化物を含む温度65
0〜1100℃の燃焼排ガス中で.燃料を空気比0.0
5〜0.60の空気量の下でアフタバーニングを行ない
,アフタバーニングされた排ガスの一部を上記火炉の燃
焼系へ再循環路を介して再循環させることを特徴とする
窒素酸化物低減法。 2 火炉の燃焼系で生成した窒素酸化物を含む温度65
0〜1100℃の燃焼排ガス中で,燃料を空気比0.0
5〜0.60の空気量の下でアフタバーニングを行ない
,アフタバーニングされた排ガスの一部を上記火炉の燃
焼系の再循環路を介して再循環させる方法において再循
環路で温度が200〜600℃に下った排ガス中で空気
比0.05〜0.60の空気量の下で更にアフタバーニ
ングを行なうことを特徴とする窒素酸化物低減法。
[Claims] 1. Temperature 65 containing nitrogen oxides generated in the combustion system of the furnace
In combustion exhaust gas at 0 to 1100℃. Fuel to air ratio 0.0
A method for reducing nitrogen oxides, characterized in that afterburning is performed under an air volume of 5 to 0.60, and a part of the afterburned exhaust gas is recirculated to the combustion system of the furnace via a recirculation path. . 2 Temperature 65 including nitrogen oxides generated in the combustion system of the furnace
In the combustion exhaust gas at 0 to 1100℃, the fuel to air ratio is 0.0.
In a method in which afterburning is performed under an air amount of 5 to 0.60, and a part of the afterburned exhaust gas is recirculated through the recirculation path of the combustion system of the above-mentioned furnace, the temperature in the recirculation path is 200 to 200. A method for reducing nitrogen oxides, characterized in that afterburning is further performed in the exhaust gas at a temperature of 600° C. under an air amount having an air ratio of 0.05 to 0.60.
JP51107894A 1976-09-10 1976-09-10 Nitrogen oxide reduction method Expired JPS5813807B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP51107894A JPS5813807B2 (en) 1976-09-10 1976-09-10 Nitrogen oxide reduction method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP51107894A JPS5813807B2 (en) 1976-09-10 1976-09-10 Nitrogen oxide reduction method

Publications (2)

Publication Number Publication Date
JPS5333421A JPS5333421A (en) 1978-03-29
JPS5813807B2 true JPS5813807B2 (en) 1983-03-16

Family

ID=14470756

Family Applications (1)

Application Number Title Priority Date Filing Date
JP51107894A Expired JPS5813807B2 (en) 1976-09-10 1976-09-10 Nitrogen oxide reduction method

Country Status (1)

Country Link
JP (1) JPS5813807B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP6277475B2 (en) * 2016-03-30 2018-02-14 和雄 宮谷 Solid fuel combustion apparatus, solid fuel combustion method, gas heating apparatus, liquid heating apparatus, power generation system, and cooling system

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5246467Y2 (en) * 1973-03-06 1977-10-21
JPS5230146Y2 (en) * 1973-05-01 1977-07-09
JPS5128363A (en) * 1974-09-04 1976-03-10 Yasue Tanaka SOJIKI

Also Published As

Publication number Publication date
JPS5333421A (en) 1978-03-29

Similar Documents

Publication Publication Date Title
JPH04227404A (en) Low nox burner and usage thereof
CN107355776B (en) Combustion system, method and application of pulverized coal boiler with ultra-low NOx emission
JP2791029B2 (en) Pulverized coal burner
JPS624606B2 (en)
JPS5813807B2 (en) Nitrogen oxide reduction method
JPS60126508A (en) Finely powdered coal burning device
JPS6249521B2 (en)
CN212390351U (en) Dimethyl ether gas boiler combustor flue gas inner loop nitrogen reduction device
JPS5977208A (en) Combustion method
JP2667607B2 (en) Structure of low NOx boiler
JPH0229368Y2 (en)
JPS58164911A (en) Denitration combustion method
JPS5888506A (en) Two-stage combustion burner
JPH0323804B2 (en)
JPS63180004A (en) Boiler combustion method
JPS58145810A (en) Combustion of coal
JPS58102006A (en) Low nox pulverized coal burner
JPH0777302A (en) Nitrogen oxide low generation boiler
JPS5634005A (en) Combustion device for low nox
JPS59205506A (en) Pulverized coal burning equipment
JPH0262766B2 (en)
JPS6026923B2 (en) Low NOx combustion equipment
JPS6012522B2 (en) combustion device
JPS5585807A (en) Low nox burner device
JPS5585805A (en) Low nox burner device