JPH0259361B2 - - Google Patents
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- Publication number
- JPH0259361B2 JPH0259361B2 JP57063853A JP6385382A JPH0259361B2 JP H0259361 B2 JPH0259361 B2 JP H0259361B2 JP 57063853 A JP57063853 A JP 57063853A JP 6385382 A JP6385382 A JP 6385382A JP H0259361 B2 JPH0259361 B2 JP H0259361B2
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- Prior art keywords
- pulverized coal
- combustion
- nozzle
- air
- nox
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Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23D—BURNERS
- F23D1/00—Burners for combustion of pulverulent fuel
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
Description
【発明の詳細な説明】
本発明は微粉炭の燃焼方法に係り、特に窒素酸
化物(以下NOxという。)を低減するに好適な方
法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for combustion of pulverized coal, and particularly to a method suitable for reducing nitrogen oxides (hereinafter referred to as NOx).
化石燃料の燃焼時に生成するNOxは、フユー
エルNOxとサーマルNOxとに分類される。フユ
ーエルNOxは燃料中に含まれる窒素分(以下N
分と称す)が酸化されて発生し、サーマルNOx
は空気中の窒素が酸化されて発生する。石炭はN
分含有量が多く、燃焼時に発生するNOxの80%
近くがフユーエルNOxである。これに対して従
来開発の進められてきた燃焼技術は、2段燃焼
法、排ガス再循環法に代表されるように、燃焼温
度を低下することにより、空気中の窒素の酸化を
抑制するサーマルNOx対策に効果のあるものが
主流である。 NOx generated during the combustion of fossil fuels is classified into fuel NOx and thermal NOx. Fuel NOx is the nitrogen content (hereinafter referred to as N) contained in fuel.
) is oxidized and generated, resulting in thermal NOx
is generated when nitrogen in the air is oxidized. Coal is N
80% of NOx generated during combustion
Fuel NOx is nearby. In contrast, combustion technologies that have been developed in the past include thermal NOx, which suppresses the oxidation of nitrogen in the air by lowering the combustion temperature, as typified by the two-stage combustion method and the exhaust gas recirculation method. The most effective measures are the ones that are effective.
微粉炭燃焼時に発生するフユーエルNOxの発
生経路は、燃焼機構にともなつて次のように説明
される。微粉炭燃焼は着火、熱分解、気体燃焼、
固体燃焼の過程から成る。燃焼の初期領域は着火
及び熱分解の進む領域であり、ここで石炭中に存
在するN分は気体として揮発するものと、固体中
に残留するものとに分かれる。熱分解に続く燃焼
領域は石炭中の揮発分が燃焼する気体燃焼と揮発
分を放出した固体が燃焼する固体燃焼が進行し、
気体として放出されたN分及び固体中のN分もそ
れぞれの燃焼領域で一部NOxに一部窒素へと変
換する。 The generation route of fuel NOx generated during pulverized coal combustion can be explained as follows in conjunction with the combustion mechanism. Pulverized coal combustion involves ignition, thermal decomposition, gaseous combustion,
It consists of the process of solid combustion. The initial region of combustion is a region where ignition and thermal decomposition proceed, and the N present in the coal is divided into those that volatilize as a gas and those that remain in solid form. In the combustion region following pyrolysis, gaseous combustion in which the volatile matter in the coal is combusted, and solid combustion in which the solids that have released the volatile matter are combusted, progress.
The N released as a gas and the N in the solid are also partially converted into NOx and partially into nitrogen in the respective combustion zones.
石炭の熱分解時に気体として放出されるN分の
中には、シアン化水素(HCN)及びアンモニア
(NH3)となるものがあり、これらの窒素化合物
は高温高酸素濃度雰囲気ではNOxに酸化される
が、適当な反応温度を設定すれば、酸素共存下で
選択的にNOxを還元し窒素(N2)とする性質を
有する。この性質を利用すれば、従来開発されて
きた2段燃焼を改良し、微粉炭燃焼の低NOx化
を図ることが可能であり、2段燃焼を原理とする
バーナが開発されている。2段燃焼は1段目の低
空気比の還元性領域で、石炭中のN分をできるだ
けN2に還元する方式であり、更にNOxの低減を
図るには、燃焼火炎内でのNOxの発生領域、
NOx還元用還元剤の生成領域、NOxの還元領域
を明確に区別し制御する必要がある。 Some of the nitrogen released as a gas during thermal decomposition of coal becomes hydrogen cyanide (HCN) and ammonia (NH 3 ), and these nitrogen compounds are oxidized to NOx in an atmosphere with high temperature and high oxygen concentration. If an appropriate reaction temperature is set, NOx can be selectively reduced to nitrogen (N 2 ) in the presence of oxygen. By utilizing this property, it is possible to improve the conventionally developed two-stage combustion and reduce NOx in pulverized coal combustion, and burners based on the principle of two-stage combustion have been developed. Two-stage combustion is a method in which the N content of the coal is reduced to N2 as much as possible in the low air ratio reducing region of the first stage.In order to further reduce NOx, NOx generation within the combustion flame is region,
It is necessary to clearly distinguish and control the generation region of the reducing agent for NOx reduction and the NOx reduction region.
また、元来サーマルNOx対策として開発され
た2段燃焼をフユーエルNOx対策用に改善した
微粉炭燃焼バーナが既に開発されている。第1図
にその1例を示す。バーナは微粉炭と1次空気か
ら成る燃料混合気を供給する微粉炭ノズル01、
2次空気ノズル02、3次空気ノズル03とから
構成される。燃料混合気と2次空気によりバーナ
先端近傍に理論空気量以下の燃焼空気量で燃焼す
る1次燃焼領域が形成され、その後流に3次空気
と1次燃焼領域からの燃焼排出物による2次燃焼
領域が形成される。1次燃焼領域では石炭中のN
分からNOxの他のアンモニア及びシアン系化合
物が発生し、2次燃焼領域でこれらの窒素化合物
が反応してNOxの一部が還元され、1次及び2
次燃焼領域と燃焼領域を分割せずに、ひとつの燃
焼領域で微粉炭を燃焼するバーナよりも発生する
NOxが低下する。 In addition, a pulverized coal combustion burner has already been developed, which is an improved version of the two-stage combustion originally developed as a measure against thermal NOx, for use as a measure against fuel NOx. An example is shown in FIG. The burner includes a pulverized coal nozzle 01 that supplies a fuel mixture consisting of pulverized coal and primary air;
It is composed of a secondary air nozzle 02 and a tertiary air nozzle 03. A primary combustion region is formed near the burner tip by the fuel mixture and secondary air, where combustion occurs with an amount of combustion air less than the stoichiometric air amount. A combustion zone is formed. In the primary combustion region, N in the coal
In addition to NOx, ammonia and cyanide compounds are generated from the minute, and these nitrogen compounds react in the secondary combustion area to reduce some of the NOx, resulting in primary and secondary combustion.
This occurs more than in a burner that burns pulverized coal in one combustion zone without dividing the next combustion zone and combustion zone.
NOx decreases.
第1図に示すバーナは、上記理由によりNOx
低減に有効であるが、1次燃焼領域での燃焼空気
量がNOx濃度及び未燃々料の排出に敏感であり、
未燃々料排出量を低減しかつNOx発生を抑制す
るには、燃焼空気量制御を厳密に行なう必要があ
る。また、更にNOx抑制効果を向上するには
NOx還元性化合物を発生する1次燃焼領域と2
次燃焼領域の区別を明確にし、2次燃焼領域を
NOx還元性反応に最適な反応条件に設定し易い
構造に改良する必要がある。 The burner shown in Figure 1 has NOx emissions due to the above reasons.
However, the amount of combustion air in the primary combustion region is sensitive to NOx concentration and unburned fuel emissions.
In order to reduce unburned fuel emissions and suppress NOx generation, it is necessary to strictly control the amount of combustion air. In addition, to further improve the NOx suppression effect,
The primary combustion zone that generates NOx reducing compounds and 2
Clarify the distinction between secondary combustion areas, and
It is necessary to improve the structure so that it is easy to set the optimal reaction conditions for the NOx reducing reaction.
本発明の目的は、NOx発生抑止効果が大であ
るとともに未燃分の排出が低減される微粉炭燃焼
方法を提供することにある。 An object of the present invention is to provide a pulverized coal combustion method that is highly effective in suppressing NOx generation and reduces emissions of unburned matter.
本発明は、2つの微粉炭供給ノズルを有するバ
ーナを用いて微粉炭を燃焼する方法において、微
粉炭とこれを搬送する空気の混合物を2系統に分
けてそれぞれのノズルに送給し、一方のノズルか
ら噴出する微粉炭を空気比1以上で燃焼させ、他
方のノズルから噴出する微粉炭を空気比1未満で
燃焼し、前記一方のノズルから噴出する微粉炭に
よる火炎と、前記他方のノズルから噴出する微粉
炭による火炎とを、それらの後流域で合体させる
ことを特徴とする微粉炭の燃焼方法である。ここ
に、空気比とは、供給される空気量を燃料を完全
燃焼させるのに必要な理論空気量で除した比であ
る。 The present invention provides a method for burning pulverized coal using a burner having two pulverized coal supply nozzles, in which a mixture of pulverized coal and air for conveying it is divided into two systems and fed to each nozzle, and one Pulverized coal ejected from one nozzle is combusted at an air ratio of 1 or more, pulverized coal ejected from the other nozzle is combusted at an air ratio of less than 1, and a flame from the pulverized coal ejected from the one nozzle and a flame from the other nozzle are generated. This is a pulverized coal combustion method characterized by merging the ejected pulverized coal with a flame in the trailing region of the pulverized coal. Here, the air ratio is a ratio obtained by dividing the amount of air to be supplied by the theoretical amount of air required to completely burn the fuel.
前述の如く、石炭中のN分は、熱分解過程にお
いて、NOx、窒素(N2)、アンモニア(NH3)、
シアン化水素(HCN)等の化合物になる。特に
これらの化合物の中でNH3が酸素共存下でも
NOxを選択的に還元する性質を有し、NOxの還
元効果の高いことは排煙脱硝技術の分野で既に公
知の事実である。従つて、酸素を含む燃焼ガス中
のNOxを石炭を利用して効果的に還元するには、
石炭からNH3を多量に発生させ、これをNOxと
反応させれば良く、石炭燃焼時のNOx低減は、
NH3の発生法及びNH3とNOxの混合法が主要な
技術課題になる。しかるに、石炭中のN分が熱分
解時に転換する窒素化合物の種類は、石炭の熱分
解条件に依存し、目的のNH3を多量に発生させ
るには、NH3生成に最適な熱分解条件を設定す
る必要がある。発明者らは鋭意検討の結果、燃焼
温度に近い温度領域では石炭熱分解雰囲気中の酸
素濃度が石炭中N分のNH3転換率に及ぼす影響
が大きく、NH3転換率を最大にする最適な酸素
濃度が存在することを微粉炭の熱分解実験により
確認した。 As mentioned above, the N content in coal is converted into NOx, nitrogen (N 2 ), ammonia (NH 3 ),
It becomes compounds such as hydrogen cyanide (HCN). In particular, among these compounds, NH 3 is
It is already a well-known fact in the field of flue gas denitrification technology that it has the property of selectively reducing NOx and has a high NOx reducing effect. Therefore, in order to effectively reduce NOx in combustion gas containing oxygen using coal,
All you have to do is generate a large amount of NH 3 from coal and react with NOx, and reduce NOx during coal combustion.
The main technical issues are how to generate NH 3 and how to mix NH 3 and NOx. However, the type of nitrogen compounds that the N content of coal converts to during pyrolysis depends on the pyrolysis conditions of the coal, and in order to generate a large amount of the desired NH 3 , it is necessary to select the optimal pyrolysis conditions for NH 3 production. Must be set. As a result of intensive studies, the inventors found that in the temperature range close to the combustion temperature, the oxygen concentration in the coal pyrolysis atmosphere has a large effect on the NH 3 conversion rate of the N component in the coal, and found that the optimum method for maximizing the NH 3 conversion rate was found. The presence of oxygen concentration was confirmed by pyrolysis experiments of pulverized coal.
本発明の要点は、石炭からの熱分解生成物を
NOxの還元に利用するため、石炭中のN分の
NH3転換率が最大になる酸素濃度雰囲気で燃焼
用石炭の一部を熱分解し、これをNOx含有燃焼
ガスと混合させることにある。 The gist of the invention is to remove pyrolysis products from coal.
N content in coal is used to reduce NOx.
The purpose is to thermally decompose a portion of the combustion coal in an oxygen-concentrated atmosphere that maximizes the NH 3 conversion rate, and mix it with NOx-containing combustion gas.
また、本発明のバーナにおいては、微粉炭燃焼
火炎が、第1次、第2次、第3次燃焼領域の3通
りの領域に区分され、燃焼火炎内でNOx発生領
域とNOx還元用微粉炭熱分解生成物発生領域、
NOx還元反応領域が明確にされる。第1次燃焼
領域は、理論空気量以上の空気で微粉炭を完全に
燃焼させる完全燃焼領域であり、ここで燃料の大
部分を燃焼させる。この領域では空気比を1以上
で燃焼させるため、燃焼灰中に残留する未燃々料
は非常に少なくなると同時に多量のNOxが発生
する。2次燃焼領域は燃焼排ガスと空気との混合
ガスで噴出される微粉炭の燃焼領域であり、ここ
では空気比が1以下の燃焼、即ち微粉炭の熱分解
が進行する。この領域は酸素不足の還元性領域で
あるため、微粉炭中のN分がNOxに酸化される
割合は非常に少なく、燃焼過程でのN分の中間生
成物である、アンモニア(NH3)、シアン化水素
(HCN)等が発生する。第3次燃焼領域は2次燃
焼領域で発生する微粉炭の熱分解生成物と1次燃
焼領域で発生するNOx及び1次燃焼領域での余
剰酸素とが反応する領域であり、ここでNOxの
還元反応と炭化水素、一酸化炭素、水素、固体中
未燃分等の酸化反応が進行する。 In addition, in the burner of the present invention, the pulverized coal combustion flame is divided into three regions: primary, secondary, and tertiary combustion regions, and within the combustion flame, there is a NOx generation region and a pulverized coal for NOx reduction. Pyrolysis product generation area,
The NOx reduction reaction region is defined. The first combustion region is a complete combustion region in which pulverized coal is completely combusted with air that is greater than or equal to the theoretical air amount, and most of the fuel is combusted here. In this region, combustion is performed at an air ratio of 1 or more, so the amount of unburned fuel remaining in the combustion ash is extremely small, and at the same time, a large amount of NOx is generated. The secondary combustion region is a combustion region of pulverized coal ejected with a mixed gas of combustion exhaust gas and air, and here combustion at an air ratio of 1 or less, that is, thermal decomposition of the pulverized coal proceeds. Since this region is a reducing region lacking oxygen, the rate at which N in pulverized coal is oxidized to NOx is extremely small, and the intermediate products of N in the combustion process, ammonia (NH 3 ), Hydrogen cyanide (HCN) etc. are generated. The tertiary combustion zone is a region where the thermal decomposition products of pulverized coal generated in the secondary combustion zone react with NOx generated in the primary combustion zone and surplus oxygen in the primary combustion zone. Reduction reactions and oxidation reactions of hydrocarbons, carbon monoxide, hydrogen, unburned matter in solids, etc. proceed.
第1次燃焼領域で完全燃焼させる微粉炭を第2
次燃焼領域で熱分解させる微粉炭よりも多くする
ことにより、未燃々料の排出を低減でき、更に第
1次燃焼領域で高温に加熱された余剰酸素で第2
次燃焼領域で発生する熱分解生成物を酸化するた
め、第3次燃焼領域での化学反応を効率良く促進
できる。さらに、2つの微粉炭ノズルを離して設
けるか、または2つの微粉炭ノズルの間から空気
を噴出させると、第1次燃焼領域と第2次燃焼領
域とを明瞭に形成できる。 The pulverized coal that is completely combusted in the primary combustion area is
By using more pulverized coal than the pulverized coal that is thermally decomposed in the secondary combustion area, it is possible to reduce the emissions of unburned fuel, and furthermore, the surplus oxygen heated to a high temperature in the primary combustion area can be used to
Since the thermal decomposition products generated in the secondary combustion zone are oxidized, the chemical reaction in the tertiary combustion zone can be efficiently promoted. Furthermore, if the two pulverized coal nozzles are provided apart or if air is ejected from between the two pulverized coal nozzles, the primary combustion area and the secondary combustion area can be clearly formed.
本発明の一実施態様においては、この酸素濃度
調整のために微粉炭燃焼排ガスを利用し、燃焼排
ガスと燃焼用空気との混合比を制御することによ
り、熱分解雰囲気中の酸素濃度が調整される。 In one embodiment of the present invention, pulverized coal combustion exhaust gas is used to adjust the oxygen concentration, and the oxygen concentration in the pyrolysis atmosphere is adjusted by controlling the mixing ratio of the combustion exhaust gas and combustion air. Ru.
また本発明の一実施態様においては、熱分解領
域の酸素濃度調整を容易にするため、上記混合気
体は、微粉炭搬送に用いられ、燃焼火炉用の微粉
炭の熱分解領域に噴出させるために用いられる。 Further, in one embodiment of the present invention, in order to facilitate the adjustment of oxygen concentration in the pyrolysis region, the above-mentioned mixed gas is used for transporting pulverized coal and injected into the pyrolysis region of pulverized coal for a combustion furnace. used.
更に本発明の効果をより有効に発揮するには、
第2次燃焼領域で熱分解させる微粉炭の噴出気
体、即ち燃焼排ガスと空気との混合気の酸素濃度
を好ましくは3〜5体積%とする。すなわち、酸
素共存下でもNOxを選択的に還元できるNH3を、
微粉炭の熱分解反応で効率良く発生させるには、
熱分解条仲を選定する必要があり、発明者らは鋭
意検討の結果、熱分解雰囲気の酸素濃度が3〜5
%の時に、NH3が最も多く微粉炭から発生する
ことを発見した。従つて、第2次燃焼領域での酸
素濃度を3〜5体積%とする、即ち混合気の酸素
濃度を3〜5体積%に空気と燃焼排ガスの混合比
を調整することにより、第3次燃焼領域で進ませ
るNOxの還元反応を効果的に促進できる。 Furthermore, in order to more effectively exhibit the effects of the present invention,
The oxygen concentration of the ejected gas of the pulverized coal to be thermally decomposed in the secondary combustion region, that is, the mixture of combustion exhaust gas and air, is preferably 3 to 5% by volume. In other words, NH 3 , which can selectively reduce NOx even in the presence of oxygen,
In order to efficiently generate pulverized coal through the thermal decomposition reaction,
It is necessary to select the pyrolysis conditions, and as a result of intensive study, the inventors found that the pyrolysis atmosphere has an oxygen concentration of 3 to 5.
%, it was discovered that NH 3 was generated most from pulverized coal. Therefore, by setting the oxygen concentration in the secondary combustion region to 3 to 5% by volume, that is, by adjusting the mixture ratio of air and combustion exhaust gas to the oxygen concentration of the air-fuel mixture to 3 to 5% by volume, the tertiary It can effectively promote the reduction reaction of NOx in the combustion region.
また、酸素共存下でNH3とNOxとを効果的に
反応させるには900℃以上の反応温度が好適であ
り、このため前記微粉炭熱分解生成物とNOx含
有燃焼ガスとは燃焼火炉内で混合し、NOxの還
元反応を進ませることが好ましい。 In addition, a reaction temperature of 900°C or higher is suitable for effectively reacting NH 3 and NOx in the coexistence of oxygen, so the pulverized coal pyrolysis products and NOx-containing combustion gas are separated in the combustion furnace. It is preferable to mix them and advance the NOx reduction reaction.
以下図面を参照して本発明のバーナの一実施態
様を説明する。第2図において、微粉炭燃焼バー
ナは2つの微粉炭ノズル12,13、2次空気ノ
ズル17、3次空気ノズル18、イグナイタ16
から構成される。微粉炭及びこれを搬送、噴出さ
せるための1次空気から成る燃料混合気を噴出さ
せる微粉炭ノズル12から、燃料微粉炭の大半が
噴出し、2次空気ノズル17、3次空気ノズル1
8から噴出する2次空気、3次空気とにより、空
気比が1以上の第1次燃焼領域21が、バーナ先
端に形成される。更に本実施例では、第1次燃焼
領域21での火炎を短炎化するとともに、他の燃
焼領域から独立させるために、2次空気ノズル1
7及び3次空気ノズル18を微粉炭ノズル12の
外周に設置され、燃焼空気に旋回流を与えるため
の、2次空気旋回羽根14及び3次空気旋回羽根
15がそれぞれのノズル内に設置されている。微
粉炭ノズル13は3次空気ノズルの外周に設置さ
れ、ノズル13より、酸素濃度が3〜5体積%に
調整された燃焼排ガスと空気との混合気と微粉炭
とから成る燃料混合気が噴出する。ノズル13か
ら噴出される燃料混合気により、第1次燃焼領域
21の外周上に第2次燃焼領域22が形成され、、
この領域で第1次燃焼領域21から伝わる熱と混
合気中に含まれる酸素とにより微粉炭の熱分解反
応が進み、還元性の熱分解生成物が発生する。 An embodiment of the burner of the present invention will be described below with reference to the drawings. In FIG. 2, the pulverized coal combustion burner includes two pulverized coal nozzles 12, 13, a secondary air nozzle 17, a tertiary air nozzle 18, and an igniter 16.
It consists of Most of the fuel pulverized coal is ejected from the pulverized coal nozzle 12 that ejects a fuel mixture consisting of pulverized coal and primary air for transporting and ejecting the pulverized coal, and the secondary air nozzle 17 and the tertiary air nozzle 1
A primary combustion region 21 having an air ratio of 1 or more is formed at the tip of the burner by the secondary air and tertiary air ejected from the burner. Furthermore, in this embodiment, in order to shorten the flame in the primary combustion region 21 and make it independent from other combustion regions, the secondary air nozzle 1 is
7 and a tertiary air nozzle 18 are installed on the outer periphery of the pulverized coal nozzle 12, and a secondary air swirl vane 14 and a tertiary air swirl vane 15 are installed in each nozzle for giving a swirling flow to the combustion air. There is. The pulverized coal nozzle 13 is installed on the outer periphery of the tertiary air nozzle, and from the nozzle 13, a fuel mixture consisting of pulverized coal and a mixture of combustion exhaust gas and air whose oxygen concentration is adjusted to 3 to 5% by volume is ejected. do. A secondary combustion area 22 is formed on the outer periphery of the primary combustion area 21 by the fuel mixture injected from the nozzle 13,
In this region, the thermal decomposition reaction of the pulverized coal progresses due to the heat transmitted from the primary combustion region 21 and the oxygen contained in the mixture, and reducing thermal decomposition products are generated.
第2次燃焼領域22で発生する還元性熱分解生
成物の酸化及び第1次燃焼領域21で発生する
NOxの還元反応の起る第3次燃焼領域23が、
第1次及び第2次燃焼領域の後流に形成される。 Oxidation of reducing pyrolysis products generated in the secondary combustion zone 22 and generated in the primary combustion zone 21
The tertiary combustion zone 23 where the NOx reduction reaction occurs is
It is formed downstream of the primary and secondary combustion areas.
実施例 1
日本国内炭及び日本国内炭を1000℃の不活性雰
囲気内で加熱して製造したチヤー(石炭熱分解時
に残留する可燃性固体)を白金製ホルダーに詰
め、1000℃に加熱した時に発生するNH3を定量
することにより、石炭中のN分及びチヤー中のN
分のNH3転換率を測定した。第3図は熱分解雰
囲気中の酸素濃度を1〜7体積%の範囲で変化さ
せ、雰囲気酸素濃度のNH3転換率への影響を検
討した結果である。横軸に熱分解時の酸素濃度、
縦軸に石炭及びチヤー中のN分のNH3転換率を
示す。第3図より明らかなように、NH3転換率
は酸素濃度の影響を大きく受け、更にNH3の転
換率を最大にする最適な酸素濃度が存在する。石
炭中N分のNH3転換率は酸素濃度約3体積%で
最大になり、チヤー中のN分は約5体積%で
NH3転換率が最大になる。Example 1 This occurred when Japanese domestic coal and char produced by heating Japanese domestic coal in an inert atmosphere at 1000°C (flammable solids remaining during coal pyrolysis) were packed in a platinum holder and heated to 1000°C. By quantifying the amount of NH3 in the coal, the N content in the coal and the N in the
The NH3 conversion rate in minutes was measured. FIG. 3 shows the results of examining the effect of atmospheric oxygen concentration on NH 3 conversion rate by varying the oxygen concentration in the pyrolysis atmosphere in the range of 1 to 7% by volume. The horizontal axis is the oxygen concentration during pyrolysis,
The vertical axis shows the NH 3 conversion rate of N in coal and coal. As is clear from FIG. 3, the NH 3 conversion rate is greatly influenced by the oxygen concentration, and there is an optimum oxygen concentration that maximizes the NH 3 conversion rate. The NH3 conversion rate for N in coal reaches its maximum at an oxygen concentration of approximately 3% by volume, and the N content in coal reaches a maximum at approximately 5% by volume.
The NH3 conversion rate is maximized.
実施例 2
第4図は、実施例1の実験結果を得た実験装置
と同一装置を用い、実施例1と同様に熱分解雰囲
気中の酸素濃度の石炭中N分のNH3転換率に及
ぼす影響をみたものである。本実施例では、石炭
種の影響を検討するために、オーストラリア炭、
中国炭の熱分解反応実験を試みた。熱分解温度は
実施例1同様1000℃である。第4図より明らかな
ように、炭種によつて多少の最適酸素濃度範囲に
違いはあるが、実施例1の日本国内炭同様、オー
ストラリア炭、中国炭とも、熱分解雰囲気の酸素
濃度が約3体積%付近で石炭中N分のNH3転換
率が最大になる。Example 2 Figure 4 shows the effect of the oxygen concentration in the pyrolysis atmosphere on the NH 3 conversion rate of the N content in the coal in the same manner as in Example 1, using the same experimental apparatus as that used to obtain the experimental results in Example 1. This is a look at the impact. In this example, in order to examine the influence of coal types, Australian coal,
We attempted a thermal decomposition reaction experiment of Chinese coal. The thermal decomposition temperature is 1000°C as in Example 1. As is clear from Figure 4, there are some differences in the optimum oxygen concentration range depending on the type of coal, but as with the Japanese domestic coal in Example 1, the oxygen concentration in the pyrolysis atmosphere for both Australian and Chinese coals is approximately The NH 3 conversion rate of N in coal reaches its maximum at around 3% by volume.
上記実施例で明らかなように、石炭の熱分解生
成物をNOxの還元剤として効果的に利用するに
は、石炭の熱分解雰囲気中の酸素濃度を最適値に
制御する必要がある。 As is clear from the above examples, in order to effectively utilize the coal pyrolysis product as a NOx reducing agent, it is necessary to control the oxygen concentration in the coal pyrolysis atmosphere to an optimal value.
本発明の微粉炭燃焼方法によれば、燃焼排ガス
と空気との混合とにより、微粉炭熱分解領域の酸
素濃度を調整し、石炭中N分のNOx還元に有効
なNH3への転換率を向上させることができるた
め、微粉炭の低NOx燃焼が可能となる。即ち、
通常の燃焼ではNOxへ転換する石炭中のN分を、
熱分解領域でNH3へ転換しこれをNOxの還元に
用いることができるため、微粉炭の燃焼を低
NOx化できる。また、本発明によれば空気比1
以上の完全燃焼領域を形成するため、未燃焼料の
排出を低減することが可能である。さらに、本発
明によれば、微粉炭を2系統に分けて燃焼させる
ことにより、一方のノズルで空気比1未満の着火
性の良い条件で火炎を形成するため、燃焼負荷が
低い場合でも、すなわち、他方ノズルから噴出す
る微粉炭とこれを搬送する空気との混合物中の微
粉炭濃度が低くても、他方のノズルからの火炎を
形成し易い。 According to the pulverized coal combustion method of the present invention, the oxygen concentration in the pulverized coal pyrolysis region is adjusted by mixing the combustion exhaust gas and air, and the conversion rate of N in the coal to NH3 , which is effective for NOx reduction, is increased. This enables low NOx combustion of pulverized coal. That is,
The N content of coal, which is converted to NOx in normal combustion, is
Since it can be converted to NH 3 in the pyrolysis region and used to reduce NOx, the combustion of pulverized coal can be reduced.
Can be converted into NOx. Further, according to the present invention, the air ratio 1
Since the above complete combustion region is formed, it is possible to reduce emissions of unburned fuel. Furthermore, according to the present invention, by combusting pulverized coal in two systems, a flame is formed in one nozzle under conditions with good ignitability with an air ratio of less than 1, so even when the combustion load is low, i.e. Even if the concentration of pulverized coal in the mixture of the pulverized coal ejected from the other nozzle and the air conveying it is low, flames from the other nozzle are likely to form.
第1図は従来の低NOxバーナの側断面図、第
2図は本発明に係るバーナの側断面図、第3図及
び第4図はNH3転換率と酸素濃度との関係を示
すグラフである。
01……微粉炭ノズル、02……2次空気ノズ
ル、03……3次空気ノズル、04……点火用バ
ーナ、05,06……旋回羽根、07……着火用
補助燃料供給孔、08……微粉炭供給孔、09…
…2次空気供給孔、10……3次空気供給孔、1
1……微粉炭供給孔、12……微粉炭ノズル、1
3……微粉炭ノズル、14……2次空気旋回羽
根、15……3次空気旋回羽根、16……イグナ
イタ、17……2次空気ノズル、18……3次空
気ノズル。
Figure 1 is a side sectional view of a conventional low NOx burner, Figure 2 is a side sectional view of a burner according to the present invention, and Figures 3 and 4 are graphs showing the relationship between NH 3 conversion rate and oxygen concentration. be. 01...Pulverized coal nozzle, 02...Secondary air nozzle, 03...Tertiary air nozzle, 04...Ignition burner, 05,06...Swirling vane, 07...Auxiliary fuel supply hole for ignition, 08... ...Pulverized coal supply hole, 09...
...Secondary air supply hole, 10...Tertiary air supply hole, 1
1...Pulverized coal supply hole, 12...Pulverized coal nozzle, 1
3...pulverized coal nozzle, 14...secondary air swirl vane, 15...tertiary air swirl vane, 16...igniter, 17...secondary air nozzle, 18...tertiary air nozzle.
Claims (1)
いて微粉炭を燃焼する方法において、微粉炭とこ
れを搬送する空気の混合物を2系統に分けてそれ
ぞれのノズルに送給し、一方のノズルから噴出す
る微粉炭を空気比1以上で燃焼させ、他方のノズ
ルから噴出する微粉炭を空気比1未満で燃焼さ
せ、前記一方のノズルから噴出する微粉炭による
火炎と、前記他方のノズルから噴出する微粉炭に
よる火炎とを、それらの後流域で合体させること
を特徴とする微粉炭の燃焼方法。 2 前記一方のノズルと前記他方のノズルとの間
から空気を噴出させることを特徴とする特許請求
の範囲第1項記載の微粉炭の燃焼方法。 3 前記一方のノズルと前記他方のノズルとを、
それぞれの火炎が直ちに混合しないように離して
設けることを特徴とする特許請求の範囲第1項記
載の微粉炭の燃焼方法。 4 2つの微粉炭供給ノズルを有するバーナを用
いて微粉炭を燃焼する方法において、微粉炭とこ
れを搬送する空気の混合物を2系統に分けてそれ
ぞれのノズルに送給し、一方のノズルから噴出す
る微粉炭を空気比1以上で燃焼させ、他方のノズ
ルからは、微粉炭搬送用の空気に燃焼排ガスを混
合して微粉炭を噴出させ、アンモニアを含む火炎
を形成するように前記微粉炭を空気比1未満で燃
焼させ、前記一方のノズルから噴出する微粉炭に
よる火炎と、前記他方のノズルから噴出する微粉
炭による火炎とを、それらの後流域で合体させる
ことを特徴とする微粉炭の燃焼方法。[Claims] 1. A method for burning pulverized coal using a burner having two pulverized coal supply nozzles, in which a mixture of pulverized coal and air for conveying the pulverized coal is divided into two systems and fed to each nozzle. , the pulverized coal ejected from one nozzle is combusted at an air ratio of 1 or more, the pulverized coal ejected from the other nozzle is combusted at an air ratio of less than 1, a flame caused by the pulverized coal ejected from the one nozzle, and the other A method of combustion of pulverized coal, characterized by combining the flame of pulverized coal ejected from a nozzle in the trailing region of the pulverized coal. 2. The pulverized coal combustion method according to claim 1, characterized in that air is ejected from between the one nozzle and the other nozzle. 3 the one nozzle and the other nozzle,
The pulverized coal combustion method according to claim 1, characterized in that the respective flames are provided separately so that they do not mix immediately. 4. In a method of burning pulverized coal using a burner having two pulverized coal supply nozzles, a mixture of pulverized coal and air carrying it is divided into two systems and fed to each nozzle, and is ejected from one nozzle. The pulverized coal is combusted at an air ratio of 1 or more, and the pulverized coal is ejected from the other nozzle by mixing combustion exhaust gas with the air for transporting the pulverized coal, and the pulverized coal is blown out to form a flame containing ammonia. The pulverized coal is burned at an air ratio of less than 1, and the flame of the pulverized coal ejected from the one nozzle and the flame of the pulverized coal ejected from the other nozzle are combined in the trailing region of the pulverized coal. Combustion method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6385382A JPS58182003A (en) | 1982-04-19 | 1982-04-19 | How to burn pulverized coal |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6385382A JPS58182003A (en) | 1982-04-19 | 1982-04-19 | How to burn pulverized coal |
Related Child Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP1858890A Division JPH0339804A (en) | 1990-01-29 | 1990-01-29 | Burner for pulverized coal combustion |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS58182003A JPS58182003A (en) | 1983-10-24 |
| JPH0259361B2 true JPH0259361B2 (en) | 1990-12-12 |
Family
ID=13241303
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP6385382A Granted JPS58182003A (en) | 1982-04-19 | 1982-04-19 | How to burn pulverized coal |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS58182003A (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS60200008A (en) * | 1984-03-22 | 1985-10-09 | Babcock Hitachi Kk | Pulverized coal burner |
| CN101949542A (en) * | 2010-04-14 | 2011-01-19 | 华中科技大学 | Three-layered secondary air low nitrogen oxide swirl burner |
| CN102434878A (en) * | 2011-09-09 | 2012-05-02 | 华中科技大学 | Three-layer secondary air low nitrogen oxide swirling burner |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS54102629A (en) * | 1978-01-31 | 1979-08-13 | Mitsubishi Heavy Ind Ltd | Burner for combustion of solid micropowder fuel |
-
1982
- 1982-04-19 JP JP6385382A patent/JPS58182003A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58182003A (en) | 1983-10-24 |
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