JPH0221107A - Low NOx combustion method for pulverized coal - Google Patents

Low NOx combustion method for pulverized coal

Info

Publication number
JPH0221107A
JPH0221107A JP13904589A JP13904589A JPH0221107A JP H0221107 A JPH0221107 A JP H0221107A JP 13904589 A JP13904589 A JP 13904589A JP 13904589 A JP13904589 A JP 13904589A JP H0221107 A JPH0221107 A JP H0221107A
Authority
JP
Japan
Prior art keywords
combustion
air
nox
burner
fuel
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.)
Pending
Application number
JP13904589A
Other languages
Japanese (ja)
Inventor
Toru Inada
徹 稲田
Norio Arashi
紀夫 嵐
Shigeru Azuhata
茂 小豆畑
Kiyoshi Narato
清 楢戸
Kenichi Soma
憲一 相馬
Yoshinobu Kobayashi
啓信 小林
Keizo Otsuka
大塚 馨象
Takao Hishinuma
孝夫 菱沼
Tadahisa Masai
政井 忠久
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.)
Hitachi Ltd
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
Hitachi 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 Babcock Hitachi KK, Hitachi Ltd filed Critical Babcock Hitachi KK
Priority to JP13904589A priority Critical patent/JPH0221107A/en
Publication of JPH0221107A publication Critical patent/JPH0221107A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To reduce NOx generated during the combustion of dust coal by turning volatile nitrogen oxides contained in the dust coal into reducing nitrogen oxides, such as NH3, and HCN in an air shortage region formed by the combustion of a main burner, and reducing NOx generated in an air excess region formed by the combustion of a sub burner. CONSTITUTION:Combustion flames formed by a main burner 52 are arranged to have an air ratio of 0.9 to 1.0 and get subjected to rather imperfect combustion, produce reducing substances generation atmosphere, and form perfect combustion state in a region where the combustion flames generated by a sub burner 53 have an excess air ratio of 1.1 and over. In other words, NOx generated by the sub burner 53 is reduced by reducing nitrogen oxides, such as NH3, and HCN so as to reduce NOx.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は微粉炭の燃焼方法に係り、特に、微粉炭の燃焼
時に発生する窒素酸化物(以下、NOxと称する)を低
減するのに好適な燃焼方法に関する。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a method for burning pulverized coal, and is particularly suitable for reducing nitrogen oxides (hereinafter referred to as NOx) generated during combustion of pulverized coal. Regarding combustion methods.

〔従来技術〕[Prior art]

化石燃料中には、C,H等の燃料成分の他にN分が含ま
れる。特に、石炭の場合には、気体燃料や液体燃料に比
較してN分合有量が多い。従って。
Fossil fuels contain N in addition to fuel components such as C and H. In particular, in the case of coal, the amount of N content is larger than that of gaseous fuel or liquid fuel. Therefore.

石炭の燃焼時に発生するNOxは、気体及び液体燃料の
燃焼時に発生するNOxよりも多く、これを極力低減す
ることが要望されている。
NOx generated during combustion of coal is greater than NOx generated during combustion of gas and liquid fuels, and it is desired to reduce this as much as possible.

種々の燃料の燃焼時に発生するNOxは、サーマルNO
xとフューエルNOxとに分類される。
NOx generated during the combustion of various fuels is thermal NOx.
It is classified into x and fuel NOx.

サーマルNOxは、燃焼用空気中の窒素が酸素によって
酸化され、生成するものであり、フューエルNOxは、
燃料中のN分の酸化により生成するものである。これら
のNOx発生を抑止するための燃焼法として、従来、燃
焼用空気を多段に分割して供給する多段燃焼法、低酸素
濃′度の燃焼排ガスを燃焼領域に混入する排ガス再循環
法等がある。
Thermal NOx is generated when nitrogen in the combustion air is oxidized by oxygen, and fuel NOx is
It is produced by the oxidation of N in fuel. Conventional combustion methods to suppress the generation of NOx include a multistage combustion method in which combustion air is divided into multiple stages and supplied, and an exhaust gas recirculation method in which combustion exhaust gas with a low oxygen concentration is mixed into the combustion area. be.

これらの低NOx燃焼法に共通な原理は、低酸素燃焼に
よって燃焼火炎の温度を下げることにより。
The common principle of these low NOx combustion methods is to lower the temperature of the combustion flame through low oxygen combustion.

窒素と酸素の反応を抑制することにある。ところで、前
記2種類のNOxの中で、燃焼温度の低下によって発生
を抑止できるのは、サーマルNOxであり、フューエル
NOxの発生は燃焼温度に対する依存性は低い。従って
火炎温度の低下を目的とする従来の燃焼法は、N分含有
量の少ない燃料からのNOx低減には有効であるが、発
生するNOxの80%近くがフューエルNOxである微
粉炭燃焼に対しては効果が小さい。
Its purpose is to suppress the reaction between nitrogen and oxygen. By the way, of the two types of NOx mentioned above, thermal NOx can be suppressed from being generated by lowering the combustion temperature, and the generation of fuel NOx is less dependent on the combustion temperature. Therefore, conventional combustion methods aimed at lowering the flame temperature are effective in reducing NOx from fuel with low N content, but compared to pulverized coal combustion, where nearly 80% of the NOx generated is fuel NOx. The effect is small.

〔発明の目的〕[Purpose of the invention]

本発明の目的は、微粉炭特有の燃焼時のフューエルNO
xの生成を考慮し、燃焼装置を大型化することなく、微
粉炭燃焼時に発生するNOxを低減するに効果的な、燃
焼方法を提供するにある。
The purpose of the present invention is to reduce the fuel NO during combustion peculiar to pulverized coal.
It is an object of the present invention to provide a combustion method that is effective in reducing NOx generated during pulverized coal combustion without increasing the size of a combustion device, taking into account the generation of x.

〔発明の概要〕[Summary of the invention]

石炭中の可燃成分は、揮発成分と固体成分とに大別でき
る。この石炭固有の性質に従い、微粉炭の燃焼機構は揮
発成分が放出される微粉炭の熱分解過程、放出された揮
発成分の燃焼過程、更に、熱分解後の可燃性固体成分(
以下チャーと称する)の燃焼過程からなる。揮発成分の
燃焼速度は固体成分の燃焼速度よりはるかに早く、揮発
成分は燃焼の初期過程で燃焼する。また、熱分解過程で
は。
Combustible components in coal can be roughly divided into volatile components and solid components. According to the unique properties of coal, the combustion mechanism of pulverized coal consists of the thermal decomposition process of pulverized coal in which volatile components are released, the combustion process of the released volatile components, and the combustion process of combustible solid components after thermal decomposition (
It consists of the combustion process of char (hereinafter referred to as char). The burning rate of volatile components is much faster than that of solid components, and volatile components are burned in the initial process of combustion. Also, in the pyrolysis process.

石炭中に含有されるN分も、他の可燃成分と同様に揮発
放出されるものとチャー中に残るものとに分かれる。従
って、微粉炭燃焼時に発生するフューエルNOxは、揮
発性N分からのNOxとチャー中のN分からのNOxと
に分かわる。この二種類のフューエルNOxの中で、チ
ャーからのフューエルNOxは、チャーが燃焼すること
によって初めて生成するため、燃焼の後半までNOxの
生成が続き、この対策が重要な鍵となる。
Like other combustible components, the N contained in coal is divided into those that are volatilized and released and those that remain in the char. Therefore, fuel NOx generated during combustion of pulverized coal is divided into NOx from volatile N and NOx from N in char. Of these two types of fuel NOx, fuel NOx from char is only generated when char is burned, so NOx continues to be generated until the latter half of combustion, and countermeasures against this are an important key.

揮発性N分は、燃焼の初期過程及び酸素不足の燃焼領域
でHNa 、 HCN等の化合物になることが知られて
いる。これらの窒素化合物は、酸素と反応してNOxに
なる他に、発生したNOxと反応してNOxを窒素に分
解する還元剤にもなり得る。この窒素化合物によるNO
x還元反応は、NOxとの共存系において進行するもの
であり、NOxが共存しない反応系では、大半の窒素化
合物はNOxに酸化される。また、この還元物質の生成
は低酸素濃度雰囲気になる程進行し易い。
It is known that volatile N becomes compounds such as HNa and HCN in the initial process of combustion and in the oxygen-deficient combustion region. These nitrogen compounds, in addition to reacting with oxygen to become NOx, can also serve as reducing agents that react with generated NOx and decompose NOx into nitrogen. NO due to this nitrogen compound
The x reduction reaction proceeds in a system in which NOx coexists, and in a reaction system in which NOx coexists, most nitrogen compounds are oxidized to NOx. Further, the generation of this reducing substance progresses more easily as the atmosphere becomes lower in oxygen concentration.

このように、微粉炭燃焼時のNOx低減法としては、還
元性をもつ揮発性窒素化合物とNOxとを共存させ、窒
素化合物によりNOxを窒素に還元する燃焼法が有効で
ある。即ち、NOxの前駆物質であるNHa等の還元性
窒素化合物をNOxの還元に利用することにより、発生
したNOxの消滅とNOx前駆物質の消滅を行なわせる
燃焼法がNOx低減には有効である。
As described above, an effective method for reducing NOx during combustion of pulverized coal is a combustion method in which a volatile nitrogen compound having reducing properties and NOx coexist and the nitrogen compound reduces NOx to nitrogen. That is, a combustion method that uses a reducing nitrogen compound such as NHa, which is a precursor of NOx, to reduce NOx, thereby eliminating the generated NOx and the NOx precursor is effective for reducing NOx.

この原理に基づき、燃料をNOx発生用と還元剤発生用
とに二段に分割供給する燃焼法が既に公知であり、例え
ば、特公昭55−21922号に示される燃焼法は、複
数個のバーナを使用し、火炉内で燃料の二段供給を行な
うものである。この燃焼法は、主バーナからの火炎を空
気比1以上にすることにより主燃焼を行なう工程、ここ
で発生したNOxを還元するために二段目のバーナから
燃料を供給して空気比1以下の還元領域を形成する工程
、更に、三段目のバーナから空気を供給し、還元領域で
の余剰燃料を燃焼する工程からなるものである。この燃
焼法によりNOx低減が可能なことはよく知られている
が、これを石炭燃焼に採用しN Ox低減効果を高める
ためには、−段目、二段目、三段目バーナ間の距雛を大
きくし、各燃焼領域の区分を明瞭にする必要があるため
、燃焼炉が大きくなり、実用上は経済的に不利になる。
Based on this principle, a combustion method in which fuel is dividedly supplied in two stages for generating NOx and for generating a reducing agent is already known. This system uses two stages of fuel supply within the furnace. This combustion method is a process in which main combustion is performed by bringing the flame from the main burner to an air ratio of 1 or more, and then fuel is supplied from the second stage burner to reduce the NOx generated in this process, and the air ratio is 1 or less. This process consists of a step of forming a reduction region, and a step of supplying air from the third stage burner to burn excess fuel in the reduction region. It is well known that this combustion method can reduce NOx, but in order to apply this method to coal combustion and increase the NOx reduction effect, it is necessary to reduce the distance between the -, second, and third stage burners. Since it is necessary to increase the size of the chicks and clearly distinguish each combustion area, the combustion furnace becomes large, which is economically disadvantageous in practical use.

更に、実機ボイラへ適用する場合、例えば、電力用の大
型ボイラでは火炉幅22m、炉奥行15.5mと燃焼炉
断面積が大きくなり、主バーすがらの主流と、炉壁に設
置した二段目、三段目バーナがら噴出させる燃料及び空
気とを完全に混合させることは困難である。故に、燃焼
炉断面内で燃料及び空気の不均一分布、これに伴ってN
Ox濃度の不均一分布が生じ、小型の試験炉で得られる
結果と同様なNOx低減効果は得られない。特に、三段
目バーナからの空気の混合が不良な時には、未燃分の放
出量が増加するため、燃焼効率の低下を生ずる。
Furthermore, when applied to an actual boiler, for example, in a large boiler for electric power, the cross-sectional area of the combustion furnace is large, with a width of 22 m and a depth of 15.5 m. It is difficult to completely mix the fuel and air ejected from the third stage burner. Therefore, the non-uniform distribution of fuel and air within the cross section of the combustion furnace and the associated N
Non-uniform distribution of Ox concentration occurs, and the same NOx reduction effect as obtained in a small test reactor cannot be obtained. In particular, when the air from the third stage burner is poorly mixed, the amount of unburned matter released increases, resulting in a decrease in combustion efficiency.

更に、複数個のバーナを組み合わせたセルバーナに上り
燃料の二段供給燃焼を行なわせるものとして、特開昭5
6−906号、特開昭56−149517号。
Furthermore, a cell burner combining a plurality of burners was developed to carry out two-stage fuel supply combustion.
No. 6-906, JP-A-56-149517.

特開昭57−1673号に示されるバーナが公知である
A burner disclosed in Japanese Patent Application Laid-Open No. 57-1673 is known.

この公知技術によれば、燃焼炉の大型化防止に有効であ
り、−火燃焼領域である主燃焼領域及び二次燃力゛む領
域である還元燃焼領域からの反応生成物の混なも公知側
特公昭55−21922号に代表される燃焼法より改善
される。しかし、還元剤とNOxの発生及び両者の混合
を理想的に具現化するには、還元剤の発生領域とNOx
発生領域の相互干渉を無くする。即ち、各反応領域での
反応終了後に各領域からの生成物を混合する必要があり
、反応途中での各領域の混合を少なくする必要′がある
According to this known technique, it is effective to prevent the combustion furnace from increasing in size, and it also prevents the mixture of reaction products from the main combustion zone, which is the fire combustion zone, and the reduction combustion zone, which is the zone containing secondary combustion. This is an improvement over the combustion method typified by Special Publication No. 55-21922. However, in order to ideally realize the generation of the reducing agent and NOx and the mixing of the two, it is necessary to
Eliminate mutual interference between generation areas. That is, it is necessary to mix the products from each reaction zone after the reaction in each zone is completed, and it is necessary to reduce the amount of mixing of each zone during the reaction.

前記公知例で、更に、NOx低減の効果を上げるには、
前述のように、空気不足燃焼領域の反応促進及び空気不
足領域からの反応生成物と空気過剰領域からの反応生成
物との混合を、更に、改善する必要がある。
In the above-mentioned known example, in order to further increase the effect of reducing NOx,
As previously mentioned, there is a need to further improve the reaction promotion of the air starved combustion zone and the mixing of reaction products from the air starved zone with reaction products from the air rich zone.

一般に、NOx低減を図ると未燃分量が増加する傾向に
あり、低NOx、低未燃分を同時に達成するには従来の
燃焼法では困難である。そこで、微粉炭燃焼の際、未燃
分の放出は50メツシュ以上の粗大粒子に左右されると
して、粉砕後の石炭を微粉と粗粉とに分離する手段を設
け、別々のバーナに粗粉と微粉とを供給し、粗粉燃焼に
際しては空気比を高くし、微粉燃焼に際しては、空気比
を低くすることにより、低NOxと低未燃分の放出を達
成する微粉炭燃焼装置が特開昭51−106241号に
述べられている。本燃焼装置は、従来の燃焼方式に比し
て、NOx低減及び未燃分の放出低減には有効であるが
、公知側特公昭55−21922号と同様に、低空気比
で燃焼する微粉燃焼火炎からの未燃分と、これを燃焼す
るための空気の混合法が問題である。
Generally, when attempting to reduce NOx, the amount of unburned substances tends to increase, and it is difficult to simultaneously achieve low NOx and low unburned substances using conventional combustion methods. Therefore, when pulverized coal is burned, the release of unburned matter depends on coarse particles of 50 mesh or more, so a means is provided to separate the pulverized coal into fine powder and coarse powder, and the coarse powder and coarse powder are placed in separate burners. A pulverized coal combustion device that achieves low NOx and low unburned emissions by supplying fine powder and increasing the air ratio during coarse powder combustion and lowering the air ratio during fine powder combustion was published in Japanese Patent Application Publication No. No. 51-106241. This combustion device is more effective in reducing NOx and reducing the release of unburned substances than conventional combustion methods, but like the publicly known Japanese Patent Publication No. 55-21922, it is a pulverized combustion device that burns at a low air ratio. The problem is how to mix the unburned material from the flame with the air used to burn it.

本発明の特徴は、燃料石炭を多段に分割して供給する燃
焼方法で、燃料石炭及び燃料石炭搬送を兼ねた一次燃焼
空気とを噴出させる円筒状バーナの中心部に設けられた
一次燃料ノズルと、燃料石炭搬送を兼ねた二次燃焼空気
とを噴出させる、次燃料ノズルと同心円になるよう、一
次燃料ノズルの外周上に設けられた旋回流発生手段を具
備した二次燃料ノズルと、三次燃焼空気を噴出させる二
次燃料ノズルの外周に設けられた旋回流発生手段を具備
した三次空気ノズルとから構成される低NOx燃焼バー
ナを、主バーナと副バーナとに二段に配置し、主バーナ
を排ガス流れについて上流に、副バーナを主バーナの下
流に設け、空気比0.9〜1.0で燃焼させた主バーナ
の燃焼排ガス中の窒素酸化物を、空気比1.1 以上で
燃焼させた副バーナの燃焼ガスで気相還元し完全燃焼さ
せることにある。
The present invention is characterized by a combustion method in which fuel coal is divided and supplied in multiple stages, and includes a primary fuel nozzle provided in the center of a cylindrical burner that blows out fuel coal and primary combustion air that also serves as fuel coal conveyance. , a secondary fuel nozzle equipped with a swirling flow generating means provided on the outer periphery of the primary fuel nozzle so as to be concentric with the secondary fuel nozzle, which blows out secondary combustion air that also serves as fuel coal conveyance, and tertiary combustion. A low NOx combustion burner consisting of a secondary fuel nozzle that blows out air and a tertiary air nozzle equipped with a swirling flow generation means provided on the outer periphery of the main burner and a sub-burner is arranged in two stages. is installed upstream of the exhaust gas flow, and a sub-burner is installed downstream of the main burner, and the nitrogen oxides in the combustion exhaust gas of the main burner are combusted at an air ratio of 1.1 or more. The purpose is to perform gas phase reduction and complete combustion using the combustion gas from the auxiliary burner.

本発明は、主バーナの燃焼によって形成される空気不足
の領域で、微粉炭中の揮発性窒素化合物をNOxOx化
することなく、N II3. HCN等の還元性窒素化
合物にし、この還元性窒素化合物により、副バーナの燃
焼によって形成される空気過剰領域で発生するN Ox
を還元する。
The present invention is capable of converting volatile nitrogen compounds in pulverized coal into NII3. Reducing nitrogen compounds such as HCN are used to reduce NOx generated in the air excess area formed by combustion in the auxiliary burner.
to reduce.

〔発明の実施例〕[Embodiments of the invention]

第1図に本発明の一実施例のバーナを示す。本バーナは
、二つの燃料石炭の噴出ノズル11゜13、三次空気ノ
ズル14及び燃焼炉予熱用燃料噴出ノズル17より構成
される。燃料石炭−は一次燃料、二次燃料に区分され、
それぞれ一次燃料ノズル11.二次燃料ノズル13より
噴出した。燃焼用空気は、一次燃料の搬送に使用する一
次空気。
FIG. 1 shows a burner according to an embodiment of the present invention. This burner is composed of two fuel coal injection nozzles 11 and 13, a tertiary air nozzle 14, and a combustion furnace preheating fuel injection nozzle 17. Thermal coal is divided into primary fuel and secondary fuel.
each primary fuel nozzle 11. It was ejected from the secondary fuel nozzle 13. Combustion air is primary air used to convey primary fuel.

二次燃料の搬送に使用する二次空気、更に三次空気に分
離し、それぞれ二次燃料ノズル11.二次燃料ノズル1
3.三次空気ノズル14より噴出した。バーナ中心には
、円筒状の燃焼炉予熱用燃料噴出ノズル17を設置し、
スタートアップ時の燃焼炉予熱時に、これより気体燃料
を噴出し、一次空気、二次空気、三次空気によって燃焼
した。燃焼炉内の温度が所定の温度に達した時に、気体
燃料の噴出を停止し、一次燃料及び二次燃料である微粉
炭をそれぞれの噴出ノズルより噴出した。
The secondary air used for conveying the secondary fuel is further separated into tertiary air, and each is connected to a secondary fuel nozzle 11. Secondary fuel nozzle 1
3. It was ejected from the tertiary air nozzle 14. A cylindrical combustion furnace preheating fuel injection nozzle 17 is installed in the center of the burner,
When the combustion furnace was preheated during startup, gaseous fuel was ejected from this and combusted using primary air, secondary air, and tertiary air. When the temperature inside the combustion furnace reached a predetermined temperature, the injection of gaseous fuel was stopped, and pulverized coal, which was the primary fuel and secondary fuel, was ejected from the respective injection nozzles.

次燃料ノズル11は、燃焼炉予熱用燃料噴出ノズル17
の外周同心円」−に配置し、燃焼炉予熱用燃料噴出ノズ
ル17を内管とし、一次燃料ノズル11を外管する二重
円筒構造となるよう、円筒状のノズルとした、二次燃料
ノズル13は、一次燃料ノズル11の外周に設置し、一
次燃料ノズル11と同心円となる環状ノズルとした。ま
た、二次燃料ノズル13の噴出口には、軸流式の旋回流
発生器15を設置し、二次燃料と二次空気とから成る混
和流に旋回流を与えて噴出した。三次空気ノズル14は
、二次燃料ノズル13の外周同心円上に設置した。三次
空気ノズル14は、八本の円管によって構成され、また
、八本の円管はピッチサークル上に等間隔に設置した。
The secondary fuel nozzle 11 is a fuel injection nozzle 17 for preheating the combustion furnace.
The secondary fuel nozzle 13 is a cylindrical nozzle arranged in a concentric circle on the outer periphery of the cylinder, and has a double cylindrical structure with the combustion furnace preheating fuel injection nozzle 17 as the inner pipe and the primary fuel nozzle 11 as the outer pipe. is an annular nozzle that is installed on the outer periphery of the primary fuel nozzle 11 and is concentric with the primary fuel nozzle 11. Further, an axial swirling flow generator 15 was installed at the ejection port of the secondary fuel nozzle 13 to give a swirling flow to the mixed flow consisting of the secondary fuel and secondary air and eject it. The tertiary air nozzle 14 was installed concentrically with the outer circumference of the secondary fuel nozzle 13. The tertiary air nozzle 14 was composed of eight circular tubes, and the eight circular tubes were installed at equal intervals on a pitch circle.

また、八本の円管はピッチサークルの接線方向に噴出口
を傾け、三次空気噴流が旋回流となるように設置した。
In addition, the eight circular pipes were installed so that the jet ports were inclined in the tangential direction of the pitch circle so that the tertiary air jet was a swirling flow.

第2図は第1図の[−n矢視図であり、第2図に三次空
気の噴出方向を矢印で示した。
FIG. 2 is a view taken along the -n arrow in FIG. 1, and the direction in which the tertiary air is ejected is indicated by an arrow.

第3図に第1図、第2図で示すバーナにより微粉炭を燃
焼した時のNOx発生量を示す。第3図の横軸は、一次
燃料と二次燃料とを完全燃焼するのに必要な理論空気量
によって、一次、二次、三次空気量の和を割った値であ
る空気比λを示し、縦軸は燃焼排ガス中のNOx濃度を
示す。使用した石炭は太平洋炭であり、200メツシユ
のふるいを約80%通過する粒径に粉砕して燃焼した。
FIG. 3 shows the amount of NOx generated when pulverized coal is burned by the burner shown in FIGS. 1 and 2. The horizontal axis in FIG. 3 indicates the air ratio λ, which is the sum of the primary, secondary, and tertiary air amounts divided by the theoretical air amount required to completely burn the primary fuel and the secondary fuel. The vertical axis indicates the NOx concentration in the combustion exhaust gas. The coal used was Taiheiyo Coal, which was pulverized to a particle size that allowed about 80% of the particles to pass through a 200-mesh sieve.

微粉炭の供給量は30kg/hであり、燃焼炉の大きさ
は、内径700nwa、長さ2mであり、第3図に示し
た実験結果31は、一次、二次燃料の供給量を等しく1
5kg/hとし、一次燃料によって形成される内炎の空
気比λ1を0.4  に設定した実験条件下で得られた
ものである。また、全体の空気比λは、三次空気量を調
整することにより変化させた。第3図より、微粉炭燃焼
時に発生するNOxは、空気比λが大きくなると増加す
ることがわかる。第3図には、本発明の効果を明らかに
するため、第1図に示したバーナを用い、供給する石炭
30kg/hを全て一次燃料とし、二次燃料を零とした
時の実験結果32も示した。第3図において、実験結果
31と32とを比較すれば明らかなように、二段燃料供
給法によれば、同一空気比において太きくNOx低減を
図れることがわかる。
The amount of pulverized coal supplied is 30 kg/h, and the size of the combustion furnace is 700 nwa in inner diameter and 2 m in length.
This was obtained under experimental conditions in which the fuel flow rate was 5 kg/h and the air ratio λ1 of the inner flame formed by the primary fuel was set to 0.4. Further, the overall air ratio λ was changed by adjusting the tertiary air amount. From FIG. 3, it can be seen that NOx generated during pulverized coal combustion increases as the air ratio λ increases. In order to clarify the effects of the present invention, Fig. 3 shows experimental results 32 using the burner shown in Fig. 1, using all of the supplied coal 30 kg/h as primary fuel, and setting the secondary fuel to zero. was also shown. As is clear from comparing experimental results 31 and 32 in FIG. 3, it can be seen that the two-stage fuel supply method allows for a greater reduction in NOx at the same air ratio.

第4図には、第3図に示した実験結果31と同一条件下
で、即ち、一次、二次燃料ともそれぞれ15kg/hの
微粉炭を供給した時の実験結果を示す。ただし、全体の
空気比λを約1.3 と一定にし、一次燃料と一次空気
で形成される内炎の空気比λl (以下、これを一次空
気比と称する)を変化させた。また、全体の空気比λを
一定に保つために、一次空気比λlの変化に伴って、三
次空気量を変化させた。第4図の横軸は一次空気比λ1
であり、縦軸は燃焼排ガス中のNOx濃度を示す。
FIG. 4 shows the experimental results under the same conditions as the experimental results 31 shown in FIG. 3, that is, when pulverized coal was supplied at a rate of 15 kg/h for both the primary and secondary fuels. However, the overall air ratio λ was kept constant at about 1.3, and the air ratio λl of the inner flame formed by the primary fuel and primary air (hereinafter referred to as the primary air ratio) was varied. Furthermore, in order to keep the overall air ratio λ constant, the tertiary air amount was changed as the primary air ratio λl changed. The horizontal axis in Figure 4 is the primary air ratio λ1
, and the vertical axis indicates the NOx concentration in the combustion exhaust gas.

第4図より、一次空気比λlには最適値が存在し、NO
xが最小になる一次空気比が存在するとことがわかる。
From Figure 4, there is an optimal value for the primary air ratio λl, and NO
It can be seen that there exists a primary air ratio where x is minimum.

このNOxが最小になる一次空気比λlの値は、一次、
二次燃料の配分比によって異なるが、1以下の値である
。この実験結果より、一次燃料で形成される内炎は還元
性雰囲気にし、二次燃料で形成される外炎は、空気比1
以上の完全燃焼領域とすることが、NOxの低減に有効
であることがわかる。
The value of the primary air ratio λl that minimizes this NOx is the primary,
Although it varies depending on the distribution ratio of the secondary fuel, it is a value of 1 or less. From this experimental result, the inner flame formed by the primary fuel is in a reducing atmosphere, and the outer flame formed by the secondary fuel has an air ratio of 1.
It can be seen that setting the complete combustion range as above is effective in reducing NOx.

そこで、低NOx燃焼方法として、二次燃料。Therefore, secondary fuel is used as a low NOx combustion method.

二次空気及び三次空気によって形成される空気比1以上
の完全燃焼領域を外炎とし、一次燃料と一次空気によっ
て形成される空気比1以下の還元性領域を内炎とする燃
料分割バーナを、主バーナと副バーナとに二段に配置し
、主バーナによる燃焼火炎を還元性雰囲気にし、副バー
ナによる燃焼火炎を完全燃焼領域にすることにより、更
に大きなNOxの低減効果を得ることがわかった。
A fuel split burner in which the complete combustion region with an air ratio of 1 or more formed by secondary air and tertiary air is an outer flame, and the reducing region with an air ratio of 1 or less formed by primary fuel and primary air is an inner flame. It was found that even greater NOx reduction effects could be obtained by arranging the main burner and the auxiliary burner in two stages, creating a reducing atmosphere for the combustion flame from the main burner, and creating a complete combustion region for the combustion flame from the auxiliary burner. .

以下、実施例により本発明を更に詳細に説明する。Hereinafter, the present invention will be explained in more detail with reference to Examples.

実施例1) 以上説明した第3図、第4図からの実験的検討結果より
、第1図のバーナを用いた場合の微粉炭の低NOx燃焼
方法のシステムを第5図に示す。
Example 1) Based on the experimental results from FIGS. 3 and 4 explained above, FIG. 5 shows a system for a low NOx combustion method for pulverized coal using the burner shown in FIG. 1.

ボイラ51に本発明のバーナ52,53を二段に配置す
る。石炭ホッパ54に貯蔵された燃料石炭55は、粉砕
機56により74μm以下の石炭が約80%を占めるよ
うに微粉化される。微粉炭の燃料石炭は、送風機57か
らの石炭搬送空気58により、主バーナ52.副バーナ
53にそれぞれ二段に分割して供給する。更に、石炭搬
送空気以外に三次空気として、送風機59からの燃焼用
空気60が主バーナ52.副バーナ53に供給される。
Burners 52 and 53 of the present invention are arranged in two stages in a boiler 51. The fuel coal 55 stored in the coal hopper 54 is pulverized by a pulverizer 56 so that about 80% of the coal is 74 μm or less. The fuel coal, which is pulverized coal, is transported to the main burner 52 by coal conveying air 58 from the blower 57. It is divided into two stages and supplied to the sub burners 53, respectively. Furthermore, combustion air 60 from the blower 59 is used as tertiary air in addition to the coal conveying air to the main burner 52. It is supplied to the auxiliary burner 53.

以上の全体構成によると、主バーナ52によって形成さ
れる燃焼火炎を、空気比0.9〜1.0にして、やや不
完全燃焼させて、還元性物質発生雰囲気とし、副バーナ
53による燃焼火炎を空気比1.1以上の過剰領域で完
全燃焼状態を形成させることにある。即ち、副バーナ5
3の燃焼によって発生するNOxを、主バーナ52の燃
焼によって生成するNHa 、HCN等の還元性窒素化
合物によって還元し、更に、NOxの低減を図る。
According to the above overall configuration, the combustion flame formed by the main burner 52 is set to an air ratio of 0.9 to 1.0 to cause a somewhat incomplete combustion to create a reducing substance generating atmosphere, and the combustion flame formed by the auxiliary burner 53 is The aim is to form a complete combustion state in an excessive air ratio of 1.1 or more. That is, the sub burner 5
The NOx generated by the combustion of No. 3 is reduced by reducing nitrogen compounds such as NHa and HCN generated by the combustion of the main burner 52, thereby further reducing NOx.

第6図に第5図で示す燃焼炉により微粉炭を燃焼した時
のNOx生成特性を示す。第6図の横軸は、主バーナの
空気比λを示し、縦軸は燃焼排ガス中のNOxを示す。
FIG. 6 shows the NOx generation characteristics when pulverized coal is burned in the combustion furnace shown in FIG. 5. The horizontal axis in FIG. 6 shows the air ratio λ of the main burner, and the vertical axis shows NOx in the combustion exhaust gas.

ただし、全体の空気比λT。However, the overall air ratio λT.

即ち、主バーナと副バーナとに供給する微粉炭の燃料石
炭を完全燃焼するのに必要な最低空気量によって、主バ
ーナと副バーナのそれぞれの一次。
That is, depending on the minimum amount of air required to completely burn the fuel coal of the pulverized coal supplied to the main burner and the auxiliary burner, the primary of each of the main burner and the auxiliary burner is determined.

二次、三次空気量の和を割った値である空気比λTを約
1.5 と一定にし、主バーナによって形成される火炎
の空気比λを変化させた。また、全体の空気比1丁を一
定に保つために、主バーナの空気比λの変化に伴って、
副バーナの空気量を変化させた。使用した石炭は一実施
例で使用した石炭と同様に太平洋炭を用いた。微粉炭の
供給量は主バーナ、副バーナ共に30 kg/ klで
あり、燃焼炉は内径1m角、高さ6mの角型竪型炉を用
いた。
The air ratio λT, which is the value obtained by dividing the sum of the secondary and tertiary air amounts, was kept constant at about 1.5, and the air ratio λ of the flame formed by the main burner was varied. In addition, in order to keep the overall air ratio constant, as the air ratio λ of the main burner changes,
The amount of air in the secondary burner was changed. The coal used was Pacific coal, similar to the coal used in one example. The amount of pulverized coal supplied to both the main burner and the auxiliary burner was 30 kg/kl, and the combustion furnace was a rectangular vertical furnace with an inner diameter of 1 m square and a height of 6 m.

第6図の実験結果は、主バーナ、副バーナとも一次、二
次燃料の供給量を等しく15kg/hとした時に得られ
たものである。第6図より、主バーナの空気比λには最
適値が存在し、NOxが最小になる主バーナの空気比λ
は0.9〜1.0の値であることがわかる。この実験結
果より、主バーナによって形成される火炎は空気比0.
9〜1.0の還元性雰囲気にすることが、N Oxの低
減に有効であることがわかる。
The experimental results shown in FIG. 6 were obtained when the primary and secondary fuel supply rates were equal to 15 kg/h for both the main burner and the auxiliary burner. From Figure 6, there is an optimum value for the main burner air ratio λ, and the main burner air ratio λ at which NOx is minimized.
It can be seen that the value is between 0.9 and 1.0. From this experimental result, the flame formed by the main burner has an air ratio of 0.
It can be seen that creating a reducing atmosphere of 9 to 1.0 is effective in reducing NOx.

第7図には、第6図と同様に第5図で示す燃焼炉により
微粉炭を燃焼とした時のNOx発生括を示す。第7図の
横軸は全体の空気比λTであり、縦軸は燃焼排ガス中の
N Ox ’a度を示す。第7図に示した実験結果75
は、主°バーナ、副バーナの一次、二次燃料共に等しく
 15 kg/ hの微粉炭を供給し、主バーナの空気
比λを0.9〜1.0とし。
Similarly to FIG. 6, FIG. 7 shows the NOx generation when pulverized coal is combusted in the combustion furnace shown in FIG. The horizontal axis in FIG. 7 represents the overall air ratio λT, and the vertical axis represents the degree of NOx 'a in the combustion exhaust gas. Experimental results 75 shown in Figure 7
In this example, 15 kg/h of pulverized coal was supplied equally to both the primary and secondary fuels of the main burner and the sub burner, and the air ratio λ of the main burner was set to 0.9 to 1.0.

副バーナの空気比λを1.1 以−ににした実験条件下
で得られたものである。また、全体の空気比λTは、副
バーナの三次空気量を調整することにより変化させた。
This was obtained under experimental conditions in which the air ratio λ of the auxiliary burner was set to 1.1 or more. Further, the overall air ratio λT was changed by adjusting the tertiary air amount of the sub-burner.

第7図より、微粉炭燃焼時に発生するNOxは、全体の
空気比を大きくすると発生量が増加する傾向にある。第
7図には1本発明の効果を明らかにするため、第5図に
示す燃焼炉を用い、供給する微粉炭の量は同じくし、主
バーナと副バーナの両バーナの空気比を1.1 以上に
して燃焼した時の実験結果76も示した。第7図におい
て、実験結果75と76とを比較すると明らかなように
、第1図に示した外炎旋回型燃料分割バーナを主バーナ
、副バーナと二段に配置し、主バーナの空気比を0.9
〜1.0、副バーナの空気比を1.1 以上にした燃焼
方法によれば、同一全空気比でも更に太き(NOxの低
減を図れることがわかる。
From FIG. 7, the amount of NOx generated during pulverized coal combustion tends to increase as the overall air ratio increases. In order to clarify the effects of the present invention, the combustion furnace shown in FIG. 5 is used, the amount of pulverized coal supplied is the same, and the air ratio of both the main burner and the auxiliary burner is set to 1. Experimental results 76 when burning at a temperature of 1 or more are also shown. As is clear from comparing experimental results 75 and 76 in FIG. 7, the external flame swirl type fuel split burner shown in FIG. 0.9
~1.0, and according to the combustion method in which the air ratio of the auxiliary burner is set to 1.1 or more, it can be seen that even with the same total air ratio, it is possible to achieve a further reduction in NOx.

次に、微粉炭燃焼時に放出される燃焼灰中未燃分量を比
較して第8図に示す。実験条件は第7図に示した実験結
果75.76と同一であり、主バーナ、副バーナとも一
次、二次燃料の供給量は等しく15kg/hである。第
8図で、実験結果81は、実験結果75の実験条件と同
一で、主バーナの空気比を0.9〜1.0とし、副バー
ナの空気比を1.1 以上にした時の燃焼実験より得ら
れたものであり、実験結果82は、実験結果76の同一
条件下、即ち、主バーナと副バーナの両バーナ共に空気
比1.1 以上で燃焼した時に得られた結果である。第
8図に示す実験結果から明らかなように1本発明の燃焼
方法によれば、同一全空気比でも燃焼灰中未燃分の放出
量も低減することができ、即ち、燃焼効率の向上を図れ
る。
Next, FIG. 8 shows a comparison of the amounts of unburned matter in the combustion ash released during pulverized coal combustion. The experimental conditions were the same as the experimental results 75.76 shown in FIG. 7, and the amounts of primary and secondary fuel supplied to the main burner and auxiliary burner were the same, 15 kg/h. In FIG. 8, experimental result 81 shows the combustion under the same experimental conditions as experimental result 75, with the air ratio of the main burner being 0.9 to 1.0 and the air ratio of the auxiliary burner being 1.1 or more. The experimental result 82 was obtained under the same conditions as the experimental result 76, that is, when both the main burner and the auxiliary burner were burned at an air ratio of 1.1 or more. As is clear from the experimental results shown in Figure 8, according to the combustion method of the present invention, the amount of unburned matter released from the combustion ash can be reduced even with the same total air ratio, that is, the combustion efficiency can be improved. I can figure it out.

本実施例によれば、第1図に示したバーナを二段に配置
することより、NOxの低減を図ることができる。この
結果、従来の多段燃焼法によって実施されてきた。完全
燃焼を行なうための空気供給用バーナを別途設ける必要
がなく、しかも、N Ha等のユーティリティ増加もな
くNOxを低減できる。従って、燃焼装置としては経済
性、容積が重要視されることは勿論であることがら、燃
焼装置の大型化を阻止できる。
According to this embodiment, NOx can be reduced by arranging the burners shown in FIG. 1 in two stages. As a result, conventional multistage combustion methods have been used. There is no need to separately provide an air supply burner for complete combustion, and NOx can be reduced without increasing utilities such as NHa. Therefore, it is possible to prevent the combustion apparatus from increasing in size, as it goes without saying that economy and volume are important considerations for the combustion apparatus.

〔発明の効果〕〔Effect of the invention〕

本発明によれば、同構造のバーナを燃焼炉内のガス流れ
に対して二段に配置することにより、微粉炭燃焼火炎を
、副バーナ燃焼によるNOx発生領域と、これを還元す
るための主バーナ燃焼による還元性物質発生領域とに明
瞭に区分でき、更に。
According to the present invention, by arranging burners with the same structure in two stages relative to the gas flow in the combustion furnace, the pulverized coal combustion flame is divided into the NOx generation area due to combustion in the auxiliary burner and the main area for reducing NOx. It can be clearly divided into the area where reducing substances are generated due to burner combustion.

両者からの反応生成物の混合を図り、NOx還元反応を
促進することができるので、燃料二段供給燃焼を効果的
に行なうことができ、NOx低減と同時に未燃分量の放
出低減を達成できる。
Since the reaction products from both can be mixed and the NOx reduction reaction can be promoted, it is possible to effectively carry out two-stage fuel supply combustion, and it is possible to achieve a reduction in NOx and at the same time a reduction in the release of unburned substances.

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

第1図は本発明の一実施例で用いるバーナの断面図、第
2図は第1図の■−■矢視図、第3図は第1図のバーナ
で石炭を燃焼した時の空気比とNOxの関係図、第4図
は第1図のバーナで石炭を燃焼した時の一次空気比とN
Oxの関係図、第5図は本発明の一実施例の全体構成を
示すフローチャート、第6図は石炭を燃焼した時の主バ
ーナの空気比とNOxとの関係図、第7図は石炭を燃焼
した時の全空気比とNOxの関係図、第8図は全空気比
と燃焼灰中未燃分の関係図である。 11・・・一次燃料ノズル、13・・・二次燃料ノズル
。 14・・・三次空気ノズル、15・・・旋回流発生器、
17・・・予熱用燃料噴出ノズル、51・・・燃焼炉。 52・・・主バーナ、53・・・副バーナ、54・・・
石炭貯量30 空気比\ 弔4図 1)で空気比χl 弔60 空気比N 率5図 弔7図 空気Fヒ 入T
Figure 1 is a cross-sectional view of a burner used in an embodiment of the present invention, Figure 2 is a view taken along the ■-■ arrow in Figure 1, and Figure 3 is the air ratio when coal is combusted with the burner in Figure 1. Figure 4 shows the relationship between primary air ratio and NOx when coal is burned in the burner shown in Figure 1.
Figure 5 is a flowchart showing the overall configuration of an embodiment of the present invention, Figure 6 is a diagram showing the relationship between NOx and the air ratio of the main burner when coal is burned, and Figure 7 is a flowchart showing the overall configuration of an embodiment of the present invention. FIG. 8 is a diagram showing the relationship between the total air ratio and NOx during combustion, and FIG. 8 is a diagram showing the relationship between the total air ratio and the unburned content in the combustion ash. 11...Primary fuel nozzle, 13...Secondary fuel nozzle. 14... Tertiary air nozzle, 15... swirl flow generator,
17... Fuel injection nozzle for preheating, 51... Combustion furnace. 52...Main burner, 53...Sub-burner, 54...
Coal storage amount 30 Air ratio \ 4 Figure 1) Air ratio χl 60 Air ratio N Rate 5 Figure 7 Air F input T

Claims (1)

【特許請求の範囲】[Claims] 1、微粉炭の燃料石炭を多段に分割して供給する燃焼方
法であつて、前記燃料石炭及び前記燃料石炭の搬送を兼
ねた一次燃焼空気とを噴出させる円筒状バーナの中心部
に設けた一次燃料ノズルと、前記燃料石炭及び前記燃料
石炭の搬送を兼ねた二次燃焼空気とを噴出させ、前記一
次燃料ノズルと同心となる様、前記一次燃料ノズルの外
周上に設けられた旋回流発生手段を具備した二次燃料ノ
ズルと、三次燃焼空気を噴出させ、前記二次燃料ノズル
の外周に設けられた旋回流発生手段を具備した三次空気
ノズルとから構成された低NO_x燃焼バーナを、主バ
ーナと副バーナとに二段に配置し、主バーナを排ガス流
れの上流に設け、副バーナを主バーナの下流に設け、空
気比0.9〜1.0で燃焼させた主バーナの燃焼排ガス
中の窒素酸化物を、空気比1.1以上で燃焼させた副バ
ーナの燃焼排ガスで還元することを特徴とする微粉炭の
低NO_x燃焼方法。
1. A combustion method in which pulverized fuel coal is divided and supplied in multiple stages, and the primary combustion air is provided in the center of a cylindrical burner that blows out the fuel coal and the primary combustion air that also serves as the conveyance of the fuel coal. Swirling flow generating means provided on the outer periphery of the primary fuel nozzle so as to eject the fuel nozzle, the fuel coal, and secondary combustion air that also serves to convey the fuel coal, and to be concentric with the primary fuel nozzle. and a tertiary air nozzle that ejects tertiary combustion air and is equipped with swirl flow generating means provided on the outer periphery of the secondary fuel nozzle. The combustion exhaust gas of the main burner is arranged in two stages, the main burner is installed upstream of the exhaust gas flow, and the auxiliary burner is installed downstream of the main burner. A low NO_x combustion method for pulverized coal, which is characterized by reducing nitrogen oxides of 20% by using combustion exhaust gas from an auxiliary burner burned at an air-to-air ratio of 1.1 or more.
JP13904589A 1989-06-02 1989-06-02 Low NOx combustion method for pulverized coal Pending JPH0221107A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13904589A JPH0221107A (en) 1989-06-02 1989-06-02 Low NOx combustion method for pulverized coal

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13904589A JPH0221107A (en) 1989-06-02 1989-06-02 Low NOx combustion method for pulverized coal

Publications (1)

Publication Number Publication Date
JPH0221107A true JPH0221107A (en) 1990-01-24

Family

ID=15236179

Family Applications (1)

Application Number Title Priority Date Filing Date
JP13904589A Pending JPH0221107A (en) 1989-06-02 1989-06-02 Low NOx combustion method for pulverized coal

Country Status (1)

Country Link
JP (1) JPH0221107A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5496188A (en) * 1992-12-09 1996-03-05 Sumitomo Wiring Systems, Ltd. Connector

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5496188A (en) * 1992-12-09 1996-03-05 Sumitomo Wiring Systems, Ltd. Connector
US5662487A (en) * 1992-12-09 1997-09-02 Sumitomo Wiring Systems, Ltd. Connector

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