JPH0618017A - Combustor - Google Patents
CombustorInfo
- Publication number
- JPH0618017A JPH0618017A JP4197537A JP19753792A JPH0618017A JP H0618017 A JPH0618017 A JP H0618017A JP 4197537 A JP4197537 A JP 4197537A JP 19753792 A JP19753792 A JP 19753792A JP H0618017 A JPH0618017 A JP H0618017A
- Authority
- JP
- Japan
- Prior art keywords
- combustion
- air
- post
- region
- fluidized bed
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/30—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having a fluidised bed
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C10/00—Fluidised bed combustion apparatus
- F23C10/18—Details; Accessories
- F23C10/20—Inlets for fluidisation air, e.g. grids; Bottoms
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C10/00—Fluidised bed combustion apparatus
- F23C10/18—Details; Accessories
- F23C10/28—Control devices specially adapted for fluidised bed, combustion apparatus
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/50—Control or safety arrangements
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/06—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2203/00—Furnace arrangements
- F23G2203/50—Fluidised bed furnace
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/34—Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
Landscapes
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Environmental & Geological Engineering (AREA)
- Incineration Of Waste (AREA)
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は都市ゴミや産業廃棄物等
を焼却する燃焼装置において、ダイオキシン等の微量な
有害物質の発生を防止すると共に、高い燃焼効率で燃焼
を行うことのできる燃焼装置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a combustion apparatus for incinerating municipal waste, industrial waste, etc., which can prevent the generation of minute amounts of harmful substances such as dioxins and can perform combustion with high combustion efficiency. It is about.
【0002】[0002]
【従来技術】近年、物流システム等の多様化により、都
市ゴミの中にプラスチック、繊維、紙等が増え、都市ゴ
ミは漸次高カロリー化の傾向にある。プラスチック類は
焼却処理の際、局部的な高温発熱により耐火材を損傷し
たり、クリンカーが発生し、炉の連続操業、ゴミの定格
量焼却を妨げるため焼却不適物として分別している治自
体もある。しかしながら、ゴミからプラスチック類を完
全に分別することが困難であり、また分離したプラスチ
ック類を埋立にしようとすると貴重なエネルギー源が埋
立処理されることにもなる。2. Description of the Related Art In recent years, due to the diversification of physical distribution systems and the like, the amount of plastics, fibers, papers and the like has increased in urban wastes, and the municipal wastes have a tendency to gradually increase in calories. During incineration of plastics, there are some cases in which refractory materials are damaged by local high-temperature heat generation, clinker is generated, and continuous operation of the furnace and incineration of the rated amount of garbage are prevented, so that plastics are sorted as unsuitable for incineration. . However, it is difficult to completely separate the plastics from the waste, and if the separated plastics are landfilled, a valuable energy source is also landfilled.
【0003】この様に高カロリー化する都市ゴミの燃焼
装置として、流動床炉を具備する燃焼装置が注目されて
いる。[0003] As a burning device for municipal wastes that have high calorie content, a burning device equipped with a fluidized bed furnace is drawing attention.
【0004】[0004]
【発明が解決しようとする課題】固形物の燃焼機構は、
水分の蒸発・乾燥工程、固形物の熱分解工程、熱分解生
成ガス及び生成チャーの燃焼工程を経て燃焼が完結す
る。流動床炉の場合は前記水分の蒸発・乾燥工程及び固
形物の熱分解工程が短時間の内に行われるため、性状の
一定していない都市ゴミの焼却の場合、生成ガス量が変
動する。このため、可燃性ガスの炉内滞留時間が一時的
に減少する。この結果として微量の未燃成分が発生す
る。特に、中規模以下のプラントでは顕著である。The combustion mechanism of solid matter is as follows:
Combustion is completed through a process of evaporating and drying water, a process of thermally decomposing solid matter, and a process of combusting pyrolysis product gas and product char. In the case of a fluidized bed furnace, the evaporation / drying process of water and the thermal decomposition process of solid matter are carried out within a short time. Therefore, in the case of incineration of municipal refuse whose properties are not constant, the amount of produced gas varies. For this reason, the residence time of the combustible gas in the furnace is temporarily reduced. As a result, a small amount of unburned components is generated. This is particularly noticeable in plants of medium scale or smaller.
【0005】一方、従来の流動床炉では、二段燃焼を行
っているがこの二段燃焼においても、フリーボード部へ
残り全量の燃焼用空気を供給するため、NOx低減に限
界があった。On the other hand, in the conventional fluidized bed furnace, two-stage combustion is performed, but even in this two-stage combustion, the remaining amount of combustion air is supplied to the freeboard section, so there is a limit to NOx reduction.
【0006】本発明は上述の点に鑑みてなされたもの
で、燃焼排ガス中に含まれる微量な未燃成分の完全燃焼
ができ、低NOx化が達成できる燃焼効率のよい燃焼装
置を提供することを目的とする。The present invention has been made in view of the above points, and provides a combustion device having a high combustion efficiency capable of completely burning a small amount of unburned components contained in combustion exhaust gas and achieving low NOx. With the goal.
【0007】[0007]
【課題を解決するための手段】上記課題を解決するため
本発明の燃焼装置は、流動床部と、その上方に位置する
フリーボード部と、未燃ガス成分を燃焼する高温領域で
ある後燃焼領域とから構成される。In order to solve the above-mentioned problems, the combustion apparatus of the present invention comprises a fluidized bed section, a freeboard section located above the fluidized bed section, and a post-combustion which is a high temperature region for burning unburned gas components. And a region.
【0008】前記燃焼装置は、フリーボード部と後燃焼
領域の接続部において、後燃焼領域入口部における断面
積ABとフリーボード部における断面積AFが次式を満足
することを特徴とする。 AF/AB≧2.5The above-mentioned combustion apparatus is characterized in that the cross-section area A B at the post-combustion area inlet and the cross-section area A F at the freeboard part satisfy the following equation at the connection portion between the freeboard section and the post-combustion area. . A F / A B ≧ 2.5
【0009】また、燃焼装置は、後燃焼領域入口部に混
合・撹拌用及び未燃ガス成分の燃焼用空気の供給を目的
として三次空気を供給することを特徴とする。Further, the combustion apparatus is characterized in that tertiary air is supplied to the inlet of the after-combustion region for the purpose of supplying air for mixing / stirring and combustion of unburned gas components.
【0010】また、燃焼装置は、フリーボード部に空気
噴射孔を有する多数のパイプを並べて構成されている混
合撹拌手段を設けたことを特徴とする。Further, the combustion apparatus is characterized in that the freeboard portion is provided with a mixing and stirring means constituted by arranging a large number of pipes having air injection holes.
【0011】また、燃焼装置は、流動床焼却部の流動床
底部から吹込む一次空気量を理論空気量以下とし、該流
動床部で燃焼物の緩慢な部分燃焼を行わせることを特徴
とする。Further, the combustor is characterized in that the amount of primary air blown from the bottom of the fluidized bed of the fluidized bed incinerator is set to be equal to or less than the theoretical amount of air so that the combusted material is slowly combusted in the fluidized bed. .
【0012】また、燃焼装置は、フリーボード部に二次
空気を吹込み、空気比を1.0〜1.5として高温酸化
雰囲気とし、更に後燃焼領域入口に三次空気を吹込むこ
とにより、当該後燃焼領域における空気比を1.5以上
とすることを特徴とする。Further, in the combustion apparatus, secondary air is blown into the freeboard portion to make a high temperature oxidizing atmosphere with an air ratio of 1.0 to 1.5, and further tertiary air is blown into the post combustion area inlet, It is characterized in that the air ratio in the post combustion region is 1.5 or more.
【0013】[0013]
【作用】本発明は燃焼装置を上記の如く構成することに
より、後燃焼領域に三次空気を供給することにより、燃
焼ガスの混合・撹拌が促進され、この結果燃焼効率が向
上する。According to the present invention, by constructing the combustion apparatus as described above, the tertiary air is supplied to the post-combustion region, whereby the mixing and stirring of the combustion gas is promoted, and as a result, the combustion efficiency is improved.
【0014】更に、後燃焼領域を設けることにより、燃
焼ガスの高温領域での滞留時間を十分にとることがで
き、未燃成分の燃焼効率が向上する。Further, by providing the post-combustion region, the residence time of the combustion gas in the high temperature region can be sufficiently secured, and the combustion efficiency of unburned components is improved.
【0015】また、フリーボード部での空気比が小さい
ので、過剰空気による冷却効果の低減ができ、フリーボ
ード部での高温化が可能となる。結果として燃焼効率が
向上する。Further, since the air ratio in the freeboard portion is small, the cooling effect due to excess air can be reduced, and the freeboard portion can be heated to a high temperature. As a result, combustion efficiency is improved.
【0016】更に、空気供給を一次空気、二次空気、三
次空気と三段階に分けて行うことにより、低NOx化が
達成できる。Further, by supplying air in three stages of primary air, secondary air, and tertiary air, NOx reduction can be achieved.
【0017】[0017]
【実施例】以下、本発明の実施例を図面に基づいて説明
する。図1は本発明の燃焼装置の構造を示す図で、図1
(A)は縦断面図、図1(B)は矢印A方向から見た側
面図である。本燃焼装置は、炉壁で囲まれた流動床部1
とその上方に位置するフリーボード部2と未燃ガス成分
を燃焼する高温領域である後燃焼領域3とから構成され
る。更に、フリーボード部2と後燃焼領域の接続部4は
燃焼排ガスの混合・撹拌の促進を目的として、フリーボ
ード部2に対して偏心させる形状としている。また、燃
焼排ガスの平均滞留時間は、フリーボード部2において
2〜4秒、後燃焼領域3及び接続部4において1〜3秒
の範囲内に設定してある。Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a diagram showing the structure of a combustion apparatus of the present invention.
1A is a vertical cross-sectional view, and FIG. 1B is a side view seen from the direction of arrow A. The combustion device is a fluidized bed 1 surrounded by a furnace wall.
And a freeboard portion 2 located above it and a post-combustion region 3 which is a high temperature region where the unburned gas component is burned. Further, the connection portion 4 between the freeboard portion 2 and the post-combustion region is shaped to be eccentric with respect to the freeboard portion 2 for the purpose of promoting mixing and stirring of combustion exhaust gas. The average retention time of the combustion exhaust gas is set within the range of 2 to 4 seconds in the freeboard section 2 and 1 to 3 seconds in the post combustion area 3 and the connecting section 4.
【0018】流動床部1の底部には一次空気7を供給す
る風箱5が設けられており、該風箱5の上部には流動床
部が形成されいる。フリーボード部2の炉壁6には二次
空気供給口8,9が設けられている。前記フリーボード
部2と後燃焼領域3の接続部4において、後燃焼領域3
の入口部における断面積ABとフリーボード部2におけ
る断面積AFが次式を満足するようになっている。 AF/AB≧2.5A wind box 5 for supplying primary air 7 is provided at the bottom of the fluidized bed 1, and a fluidized bed is formed at the top of the wind box 5. Secondary air supply ports 8 and 9 are provided in the furnace wall 6 of the freeboard unit 2. At the connecting portion 4 between the freeboard portion 2 and the post combustion region 3, the post combustion region 3
The cross-sectional area A B at the entrance portion of and the cross-sectional area A F at the freeboard portion 2 satisfy the following equation. A F / A B ≧ 2.5
【0019】また、フリーボード部2の炉壁6にはゴミ
供給口10が設けられている。更に後燃焼領域3の入口
部には三次空気供給口11が設けられており、該三次空
気供給口11から三次空気を供給することにより、燃焼
ガスの混合・撹拌が行われる。後燃焼領域3の上部は排
ガス排出口12に接続されている。以下、上記構造の燃
焼装置の動作について説明する。A dust supply port 10 is provided on the furnace wall 6 of the freeboard section 2. Furthermore, a tertiary air supply port 11 is provided at the inlet of the post combustion region 3, and by supplying the tertiary air from the tertiary air supply port 11, the combustion gas is mixed and stirred. The upper portion of the post combustion region 3 is connected to the exhaust gas outlet 12. The operation of the combustion device having the above structure will be described below.
【0020】固形物の燃焼は前述のように、(1)水分
の蒸発及び乾燥工程、(2)固形物の熱分解工程、
(3)熱分解生成ガス及び生成チャーの燃焼工程を経て
燃焼が完結する。ゴミはゴミ供給口10から高温で均一
な温度を有する流動床部1の流動媒体(砂)中へ供給さ
れる。ゴミ中に含まれる可燃性物質は上記(1),
(2),(3)の3つの工程を経るため、流動床部1の
底部から排出される残渣中には可燃物は皆無といってよ
い。As described above, the burning of the solid matter includes (1) the evaporation and drying steps of water, (2) the pyrolysis step of the solid matter,
(3) Combustion is completed through a combustion process of pyrolysis product gas and product char. The dust is supplied from the dust supply port 10 into the fluid medium (sand) of the fluidized bed 1 having a high temperature and a uniform temperature. The combustible substances contained in the garbage are (1) above,
Since the three steps of (2) and (3) are performed, it can be said that there are no combustible substances in the residue discharged from the bottom of the fluidized bed 1.
【0021】しかしながら上記(1),(2)の2工程
が短時間で行われるため、性状が一定していない都市ゴ
ミの場合は、生成ガスの変動として表われる。その結果
炉内の燃焼に必要な酸素濃度の変動が生じる。即ち燃焼
用空気(酸素)が過剰になり燃焼温度が低下したり、逆
に酸素不足となり未燃のまま大気へ放出される等の問題
が生じる。更に炉形状及びガス混合等に起因して炉内で
の酸素分布の不均一が生じ、結果として未燃成分が排ガ
ス中に含まれる。However, since the above-mentioned two steps (1) and (2) are performed in a short time, in the case of city refuse whose properties are not constant, it appears as a fluctuation of the produced gas. As a result, the oxygen concentration required for combustion in the furnace fluctuates. That is, there is a problem that the combustion air (oxygen) becomes excessive and the combustion temperature lowers, or conversely, oxygen becomes insufficient and is released into the atmosphere as unburned. Further, due to the shape of the furnace, gas mixture, etc., the oxygen distribution in the furnace becomes uneven, and as a result, unburned components are contained in the exhaust gas.
【0022】この問題を解決するため本燃焼装置では、
フリーボード部2の上部に後燃焼領域3を設けている。
この後燃焼領域3を設けることにより、(1)入口部で
の整流作用、(2)入口部での三次空気供給口11から
の三次空気流入による混合作用、(3)高温領域である
後燃焼領域3での排ガス滞留時間を確保することによ
り、拡散燃焼作用が期待できる。In order to solve this problem, in the present combustion device,
A post-combustion region 3 is provided above the freeboard unit 2.
By providing the post-combustion region 3, (1) rectifying action at the inlet part, (2) mixing action by tertiary air inflow from the tertiary air supply port 11 at the inlet part, (3) post-combustion in the high temperature region By ensuring the exhaust gas retention time in the region 3, a diffusion combustion action can be expected.
【0023】本燃焼装置は高温領域(燃焼領域)を流動
床部1、フリーボード部2及び後燃焼領域3の3つの領
域に分け、それぞれ分担役割を持って運転している。流
動床部1、フリーボード部2及び後燃焼領域3の各々に
おける運転条件基準は下記のように設定する。In the present combustion apparatus, the high temperature region (combustion region) is divided into three regions of the fluidized bed portion 1, the freeboard portion 2 and the post combustion region 3 and each of them operates in a sharing role. The operating condition criteria in each of the fluidized bed section 1, the freeboard section 2 and the afterburning zone 3 are set as follows.
【0024】(1)温度範囲の設定基準 a)流動床部1の温度はゴミのガス化速度をより緩慢に
するために、低温の方が好ましく、本実施例では上限を
700℃に設定した。一方下限は都市ゴミを構成する物
質のガス化温度に支配される。ガス化が完全に行われ、
不燃物の熱灼減量が極めて少ないことが重要である。
紙、プラスチック等都市ゴミを構成する物質の熱分解温
度は大部分が400℃以下であり、本実施例では十分な
余裕をみて下限を600℃に設定した。 b)フリーボード部2と後燃焼領域3の温度はサーマル
NOxの発生を抑制し、更に飛灰によるダスト問題を防
止するため上限を950℃に設定した。一方下限は良好
な燃焼状態を確保するため800℃以上に設定した。(1) Criteria for setting the temperature range a) The temperature of the fluidized bed 1 is preferably low in order to make the gasification rate of dust slower, and in this embodiment, the upper limit was set to 700 ° C. . On the other hand, the lower limit is governed by the gasification temperature of the substances that make up municipal waste. Complete gasification,
It is important that the amount of incombustibles burned off is extremely small.
Most of the thermal decomposition temperatures of the substances that compose the municipal waste such as paper and plastic are 400 ° C. or lower, and in this example, the lower limit was set to 600 ° C. with a sufficient margin. b) The upper limits of the temperatures of the freeboard section 2 and the post-combustion region 3 are set to 950 ° C. in order to suppress the generation of thermal NOx and prevent the dust problem due to fly ash. On the other hand, the lower limit was set to 800 ° C or higher in order to secure a good combustion state.
【0025】(2)空気比の設定基準 a)流動床部1の空気比{供給空気量:燃焼物の燃焼に
必要な最小空気量(理論空気量)}、即ち流動床部1の
底部から吹込む一次空気量の上限は、ゴミの部分燃焼を
行わせるために空気比1以下に設定した。一方、下限は
流動媒体を流動化させるのに必要な空気量に設定する。 b)フリーボード部2の空気比は高温燃焼を可能とする
と同時に、低NOx化を図るため空気比を1.0〜1.
5の領域の高温酸化雰囲気に設定した。 c)後燃焼領域3の空気比は微量の未燃成分の燃焼が完
結するために必要な量であり、後燃焼領域3の入口の三
次空気供給口11から三次空気を吹込むことにより、後
燃焼領域3における空気比を1.5以上に設定する。(2) Criteria for setting the air ratio a) Air ratio of the fluidized bed section 1 {Supply air quantity: Minimum air quantity (theoretical air quantity) required for combustion of combustion products}, that is, from the bottom of the fluidized bed section 1 The upper limit of the amount of primary air to be blown was set to an air ratio of 1 or less in order to cause partial combustion of dust. On the other hand, the lower limit is set to the amount of air required to fluidize the fluidized medium. b) The air ratio of the freeboard portion 2 enables high temperature combustion, and at the same time, the air ratio is 1.0 to 1.
The high temperature oxidizing atmosphere in the region 5 was set. c) The air ratio in the post combustion region 3 is an amount necessary for completing the combustion of a small amount of unburned components, and by blowing the tertiary air from the tertiary air supply port 11 at the inlet of the post combustion region 3, The air ratio in the combustion area 3 is set to 1.5 or more.
【0026】二次空気及び三次空気の予熱 二次空気供給口8,9及び三次空気供給口11から供給
される二次空気及び三次空気は燃焼を効率良く完結させ
るため、温度維持と撹拌作用を行わせる必要がある。本
実施例では二次空気供給口8,9及び三次空気供給口1
1から供給される二次空気及び三次空気を予熱すること
により、フリーボード部2及び後燃焼領域3の内部の高
温化とこれら二次空気及び三次空気により燃焼ガスの撹
拌を行った。また、二次空気を予熱することにより、低
発熱量ゴミでも高温燃焼が可能であり、またゴミ供給量
の変動及びゴミ性状の変動からくる燃焼ガス量変動にと
もなう二次空気による過冷却を防止でき、安定した燃焼
が確保できる。Preheating of Secondary Air and Tertiary Air The secondary air and the tertiary air supplied from the secondary air supply ports 8 and 9 and the tertiary air supply port 11 complete the combustion efficiently and therefore maintain the temperature and agitate. It needs to be done. In this embodiment, the secondary air supply ports 8 and 9 and the tertiary air supply port 1
By preheating the secondary air and the tertiary air supplied from No. 1, the internal temperature of the freeboard section 2 and the post combustion region 3 was raised, and the combustion gas was stirred by the secondary air and the tertiary air. In addition, by preheating the secondary air, it is possible to burn high-temperature dust even with low heat value, and prevent overcooling by secondary air due to fluctuations in the amount of combustion gas due to fluctuations in the amount of dust supplied and changes in dust properties. Yes, stable combustion can be secured.
【0027】図2は本発明の燃焼装置の他の構造を示す
図で、図2(A)は縦断面図、図2(B)は矢印A方向
から見た側面図である。本燃焼装置は、炉壁で囲まれた
流動床部1とその上方に位置するフリーボード部2と未
燃ガス成分を燃焼する高温領域である後燃焼領域3とか
ら構成される点は、図1の燃焼装置と同じである。本燃
焼装置が図1の燃焼装置と異なる点は、フリーボード部
2に空気噴射孔を有する多数のパイプ13を並べて配置
している点である。これによりフリーボード部2での燃
焼ガスの混合撹拌作用を向上させている。FIG. 2 is a view showing another structure of the combustion apparatus of the present invention, FIG. 2 (A) is a longitudinal sectional view, and FIG. 2 (B) is a side view seen from the direction of arrow A. The present combustion apparatus is composed of a fluidized bed portion 1 surrounded by a furnace wall, a freeboard portion 2 located above the fluidized bed portion 1, and a post combustion region 3 which is a high temperature region for burning unburned gas components. It is the same as the combustion device of No. 1. This combustion apparatus is different from the combustion apparatus of FIG. 1 in that a large number of pipes 13 having air injection holes are arranged side by side on the freeboard portion 2. This improves the mixing and stirring action of the combustion gas in the freeboard section 2.
【0028】[0028]
【発明の効果】以上説明したように本発明によれば下記
のような優れた効果が期待できる。 (1)後燃焼領域に三次空気を供給することにより、燃
焼ガスの混合・撹拌が促進され、この結果燃焼効率が向
上する。 (2)後燃焼領域を設けることにより、燃焼ガスの高温
領域での滞留時間を十分にとることができ、未燃成分の
燃焼効率が向上する。 (3)フリーボード部での空気比が小さいので、過剰空
気による冷却効果の低減ができ、フリーボード部での高
温化が可能となる。結果として燃焼効率が向上する。 (4)空気供給を一次空気、二次空気、三次空気と三段
階に分けて行うことにより、低NOx化が達成できる。As described above, according to the present invention, the following excellent effects can be expected. (1) By supplying the tertiary air to the post-combustion region, mixing and agitation of combustion gas are promoted, and as a result, combustion efficiency is improved. (2) By providing the post-combustion region, the residence time of the combustion gas in the high temperature region can be sufficiently secured, and the combustion efficiency of unburned components is improved. (3) Since the air ratio in the freeboard portion is small, the cooling effect due to excess air can be reduced, and the freeboard portion can be heated to a high temperature. As a result, combustion efficiency is improved. (4) The NOx reduction can be achieved by supplying air in three stages of primary air, secondary air, and tertiary air.
【図1】本発明の燃焼装置の構造を示す図で、図1
(A)は縦断面図、図1(B)は矢印A方向から見た側
面図である。FIG. 1 is a diagram showing the structure of a combustion apparatus of the present invention.
1A is a vertical cross-sectional view, and FIG. 1B is a side view seen from the direction of arrow A.
【図2】本発明の燃焼装置の他の構造を示す図で、図2
(A)は縦断面図、図2(B)は矢印A方向から見た側
面図である。FIG. 2 is a diagram showing another structure of the combustion apparatus of the present invention.
FIG. 2A is a vertical sectional view, and FIG. 2B is a side view seen from the direction of arrow A.
1 流動床部 2 フリーボード部 3 後燃焼領域 4 接続部 5 風箱 6 炉壁 7 一次空気 8 二次空気供給口 9 二次空気供給口 10 ゴミ供給口 11 三次空気供給口 12 排ガス排出口 13 空気噴射孔を有するパイプ 1 Fluidized Bed Part 2 Freeboard Part 3 Post-Combustion Area 4 Connection Part 5 Air Box 6 Furnace Wall 7 Primary Air 8 Secondary Air Supply Port 9 Secondary Air Supply Port 10 Dust Supply Port 11 Tertiary Air Supply Port 12 Exhaust Gas Exhaust Port 13 Pipe with air injection holes
フロントページの続き (72)発明者 山本 充利 東京都大田区羽田旭町11番1号 株式会社 荏原製作所内Front page continuation (72) Inventor Mitsutoshi Yamamoto 11-1 Haneda-Asahi-cho, Ota-ku, Tokyo Inside EBARA CORPORATION
Claims (6)
ボード部と、未燃ガス成分を燃焼する高温領域である後
燃焼領域とから構成されることを特徴とする燃焼装置。1. A combustion apparatus comprising a fluidized bed portion, a freeboard portion located above the fluidized bed portion, and a post-combustion region which is a high temperature region for burning unburned gas components.
部において、後燃焼領域入口部における断面積ABとフ
リーボード部における断面積AFが次式を満足すること
を特徴とする請求項1記載の燃焼装置。 AF/AB≧2.52. The cross-sectional area A B at the inlet of the post-combustion region and the cross-sectional area A F at the freeboard portion of the connection portion between the freeboard portion and the post-combustion region satisfy the following equation. The combustion device according to 1. A F / A B ≧ 2.5
び未燃ガス成分の燃焼用空気の供給を目的として三次空
気を供給することを特徴とする請求項1又は2記載の燃
焼装置。3. The combustion apparatus according to claim 1, wherein tertiary air is supplied to the inlet of the post-combustion region for the purpose of supplying mixing / stirring and combustion air of unburned gas components.
る多数のパイプを並べて構成されている混合撹拌手段を
設けたことを特徴とする請求項1乃至3のいずれか1つ
に記載の燃焼装置。4. The combustion apparatus according to claim 1, wherein the freeboard portion is provided with a mixing and stirring means configured by arranging a large number of pipes having air injection holes. .
量を理論空気量以下とし、該流動床部で燃焼物の緩慢な
部分燃焼を行わせることを特徴とする請求項1乃至4の
いずれか1つに記載の燃焼装置。5. The method according to claim 1, wherein the amount of primary air blown from the bottom of the fluidized bed is made equal to or less than the theoretical amount of air, and the fluidized bed is made to perform slow partial combustion. The combustion device according to any one of claims.
み、空気比を1.0〜1.5として高温酸化雰囲気と
し、更に前記後燃焼領域入口に三次空気を吹込むことに
より、当該後燃焼領域における空気比を1.5以上とす
ることを特徴とする請求項3又は4又は5記載の燃焼装
置。6. Secondary air is blown into the freeboard section to create a high temperature oxidizing atmosphere with an air ratio of 1.0 to 1.5, and further tertiary air is blown into the post combustion region inlet, thereby The combustion apparatus according to claim 3, 4 or 5, wherein the air ratio in the combustion region is 1.5 or more.
Priority Applications (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4197537A JP2707186B2 (en) | 1992-07-01 | 1992-07-01 | Combustion equipment |
TW082104695A TW228023B (en) | 1992-07-01 | 1993-06-14 | Incinerator device |
KR1019930011083A KR940005920A (en) | 1992-07-01 | 1993-06-18 | Combustion device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4197537A JP2707186B2 (en) | 1992-07-01 | 1992-07-01 | Combustion equipment |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH0618017A true JPH0618017A (en) | 1994-01-25 |
JP2707186B2 JP2707186B2 (en) | 1998-01-28 |
Family
ID=16376128
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP4197537A Expired - Lifetime JP2707186B2 (en) | 1992-07-01 | 1992-07-01 | Combustion equipment |
Country Status (3)
Country | Link |
---|---|
JP (1) | JP2707186B2 (en) |
KR (1) | KR940005920A (en) |
TW (1) | TW228023B (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2014037956A (en) * | 2012-07-20 | 2014-02-27 | Ebara Environmental Plant Co Ltd | Waste processing method and waste incinerator |
JP2014040938A (en) * | 2012-08-21 | 2014-03-06 | Kiyoshi Asai | Structure of fluidized bed type thermal reaction apparatus and treatment method of waste in the structure |
JP6322327B1 (en) * | 2017-10-11 | 2018-05-09 | 株式会社神鋼環境ソリューション | Method for supplying oxygen-containing gas to fluidized bed gasifier and fluidized bed gasifier |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS4944304U (en) * | 1972-07-20 | 1974-04-18 | ||
JPS5138719U (en) * | 1974-09-18 | 1976-03-23 | ||
JPS58156107A (en) * | 1982-03-11 | 1983-09-17 | Ishikawajima Harima Heavy Ind Co Ltd | Fluidized bed type combustion furnace |
JPS63279013A (en) * | 1987-05-07 | 1988-11-16 | Ebara Corp | Supressor for nox and unburnt gas in fluidized bed incinerator |
JPH01225802A (en) * | 1988-03-04 | 1989-09-08 | Nkk Corp | Fluidized bed type combustion furnace |
JPH0212429U (en) * | 1988-07-05 | 1990-01-25 | ||
JPH03271610A (en) * | 1990-03-20 | 1991-12-03 | Mitsui Eng & Shipbuild Co Ltd | Waste incinerator |
-
1992
- 1992-07-01 JP JP4197537A patent/JP2707186B2/en not_active Expired - Lifetime
-
1993
- 1993-06-14 TW TW082104695A patent/TW228023B/en active
- 1993-06-18 KR KR1019930011083A patent/KR940005920A/en not_active Application Discontinuation
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS4944304U (en) * | 1972-07-20 | 1974-04-18 | ||
JPS5138719U (en) * | 1974-09-18 | 1976-03-23 | ||
JPS58156107A (en) * | 1982-03-11 | 1983-09-17 | Ishikawajima Harima Heavy Ind Co Ltd | Fluidized bed type combustion furnace |
JPS63279013A (en) * | 1987-05-07 | 1988-11-16 | Ebara Corp | Supressor for nox and unburnt gas in fluidized bed incinerator |
JPH01225802A (en) * | 1988-03-04 | 1989-09-08 | Nkk Corp | Fluidized bed type combustion furnace |
JPH0212429U (en) * | 1988-07-05 | 1990-01-25 | ||
JPH03271610A (en) * | 1990-03-20 | 1991-12-03 | Mitsui Eng & Shipbuild Co Ltd | Waste incinerator |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2014037956A (en) * | 2012-07-20 | 2014-02-27 | Ebara Environmental Plant Co Ltd | Waste processing method and waste incinerator |
JP2014040938A (en) * | 2012-08-21 | 2014-03-06 | Kiyoshi Asai | Structure of fluidized bed type thermal reaction apparatus and treatment method of waste in the structure |
JP6322327B1 (en) * | 2017-10-11 | 2018-05-09 | 株式会社神鋼環境ソリューション | Method for supplying oxygen-containing gas to fluidized bed gasifier and fluidized bed gasifier |
JP2019070505A (en) * | 2017-10-11 | 2019-05-09 | 株式会社神鋼環境ソリューション | Method for supplying oxygen-containing gas to fluid bed type gasification furnace, and fluid bed type gasification furnace |
Also Published As
Publication number | Publication date |
---|---|
TW228023B (en) | 1994-08-11 |
KR940005920A (en) | 1994-03-22 |
JP2707186B2 (en) | 1998-01-28 |
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