JPH04350409A - Circulating fluidized bed type incinerator - Google Patents

Circulating fluidized bed type incinerator

Info

Publication number
JPH04350409A
JPH04350409A JP3124054A JP12405491A JPH04350409A JP H04350409 A JPH04350409 A JP H04350409A JP 3124054 A JP3124054 A JP 3124054A JP 12405491 A JP12405491 A JP 12405491A JP H04350409 A JPH04350409 A JP H04350409A
Authority
JP
Japan
Prior art keywords
incinerator
fluidized bed
furnace
main
pyrolysis
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.)
Withdrawn
Application number
JP3124054A
Other languages
Japanese (ja)
Inventor
Toshihiko Yasuda
俊彦 安田
Kenji Yasuda
賢士 保田
Jinshiro Fujita
藤田 仁四郎
Kiichi Matsuoka
松岡 喜一
Toshio Hama
利雄 濱
Kazunori Koba
木場 和則
Kanji Ota
太田 完志
Naoko Hirata
平田 直子
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 Zosen Corp
Original Assignee
Hitachi Zosen Corp
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 Hitachi Zosen Corp filed Critical Hitachi Zosen Corp
Priority to JP3124054A priority Critical patent/JPH04350409A/en
Publication of JPH04350409A publication Critical patent/JPH04350409A/en
Withdrawn legal-status Critical Current

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  • Incineration Of Waste (AREA)
  • Fluidized-Bed Combustion And Resonant Combustion (AREA)
  • Treating Waste Gases (AREA)

Abstract

PURPOSE:To provide an incinerator capable of being sufficiently adapted for a regulation over a discharging of dioxin by accommodating a circulating fluidized bed type combustion furnace of which high efficient combustion can be expected at a high probability to the incinerator for city-dust and the like and in which chlorine becoming a cause of occurrence of dioxin is easily removed at a stage of thermal decomposition gas without using any special desalting agent. CONSTITUTION:A circulating fluidized bed type incinerator is comprised of a main incinerator 1 for igniting ignited material within a high-speed fluidized bed, a cyclone 2 for collecting flowing medium particles discharged from the main incinerator 1, a thermal decomposing furnace 3 having an ignited material feeding part 31 and for thermally decomposing the ignited material with heat got from the flowing medium particles, a pneumatic control valve 4 for controlling flowing medium particles and the ignited material to be supplied to the main incinerator 1, a thermal decomposing gas supplying flow passage 5 for supplying the thermal decomposed gas generated from the thermal decomposing furnace 3 to the main incinerator 1 and a thermal decomposing gas cooling part 6 disposed in the thermal decomposing gas supplying flow passage 5.

Description

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

【0001】0001

【産業上の利用分野】この発明は、都市ごみ等の焼却炉
に関し、更に詳しくは循環流動床型焼却炉に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an incinerator for municipal waste, and more particularly to a circulating fluidized bed incinerator.

【0002】0002

【従来の技術】都市ごみ等を焼却する焼却炉においては
、ここ数年来、ダイオキシンの排出抑制等のため、焼却
による一酸化炭素の排出レベルを低減させる高効率燃焼
の必要性が叫ばれ、そのため従来から採用されている気
泡流動床型焼却炉においても、様々な改良が施されてい
る。しかしながら、それらはいずれも炉形状や空気分散
機構が複雑なものにならざるを得ず、本来気泡流動床型
焼却炉の利点であった簡便性が失われ、またこれらの改
良によっても、高効率燃焼が確実に達成されるかどうか
不明な点が多い。
[Prior Art] For the past few years, in incinerators that incinerate municipal waste, etc., there has been a need for high-efficiency combustion to reduce the level of carbon monoxide emissions from incineration, in order to suppress dioxin emissions, etc. Various improvements have been made to the conventional bubbling fluidized bed incinerator. However, all of these require complicated furnace shapes and air distribution mechanisms, and the simplicity that was originally an advantage of bubbling fluidized bed incinerators is lost, and even with these improvements, high efficiency cannot be achieved. There are many uncertainties as to whether combustion will be reliably achieved.

【0003】ところで、石炭等を燃料とする燃焼炉にお
いては、燃料適応範囲の広さ、低公害性能等の点から、
循環流動床型燃焼炉が急速にそのシェアを拡大している
[0003] Incidentally, in combustion furnaces that use coal or the like as fuel, there are
Circulating fluidized bed combustion furnaces are rapidly expanding their market share.

【0004】循環流動床型燃焼炉には、種々の形態のも
のがあるが、一般的には、ケイ砂等の耐火性粒子からな
る流動媒体粒子を炉内への空気噴出等による流動化手段
によって高速流動化させて高速流動床を形成し、この流
動床において燃料を燃焼させる主燃焼炉と、主燃焼炉か
ら排出される流動媒体粒子を排ガスと分離させて捕集す
るサイクロンと、サイクロンにより捕集された流動媒体
粒子の温度を制御する外部熱交換器と、外部熱交換器か
ら主燃焼炉へ供給される流動媒体粒子の量を制御する空
気式制御バルブとで主として構成されている。燃料とな
る石炭等は、主燃焼炉に投入されて、主燃焼炉、サイク
ロン、外部熱交換器および空気式制御バルブよりなる循
環経路を流動媒体粒子とともに循環し、燃焼される。
[0004] There are various types of circulating fluidized bed combustion furnaces, but in general, fluidized medium particles made of refractory particles such as silica sand are fluidized by blowing air into the furnace. A main combustion furnace that fluidizes the fuel at high speed to form a high-speed fluidized bed and burns the fuel in this fluidized bed, a cyclone that separates and collects the fluidized medium particles discharged from the main combustion furnace from the exhaust gas, and a cyclone that It mainly consists of an external heat exchanger that controls the temperature of the collected fluidized media particles and a pneumatic control valve that controls the amount of fluidized media particles supplied from the external heat exchanger to the main combustion furnace. Coal or the like serving as fuel is charged into the main combustion furnace, circulates along with fluidized medium particles through a circulation path consisting of the main combustion furnace, a cyclone, an external heat exchanger, and a pneumatic control valve, and is burned.

【0005】[0005]

【発明が解決しようとする課題】しかしながら、都市ご
み等の焼却にあっては、被焼却物の性状が非常に多種多
様であるために安定した高速流動化状態が阻害される懸
念があることや、構造が複雑になりがちであること等の
理由により、循環流動床型燃焼炉は、高効率燃焼が期待
されるにもかかわらず、これまで焼却炉としては採用さ
れていなかった。この発明の目的は、上記の実情に鑑み
て、高効率燃焼が高い確度で期待できる循環流動床型燃
焼炉を都市ごみ等の焼却炉に適応させて、今後よりいっ
そう厳しい規制が予想されるダイオキシン排出規制に十
分対応させるとともに、ダイオキシンの発生要因となる
塩素を、特別な脱塩剤を用いることなく容易に除去する
ことのできる焼却炉を提供することにある。
[Problem to be Solved by the Invention] However, when incinerating municipal waste, etc., there is a concern that a stable high-speed fluidization state may be hindered because the properties of the incinerated materials vary widely. Due to reasons such as the fact that the structure tends to be complicated, circulating fluidized bed combustion furnaces have not been used as incinerators until now, even though they are expected to provide highly efficient combustion. In view of the above-mentioned circumstances, the purpose of this invention is to adapt a circulating fluidized bed combustion furnace, which can be expected to achieve highly efficient combustion with a high degree of certainty, to an incinerator for municipal waste, etc., and to reduce dioxins, which are expected to be subject to stricter regulations in the future. An object of the present invention is to provide an incinerator that satisfactorily complies with emission regulations and can easily remove chlorine, which is a factor in the generation of dioxins, without using a special desalination agent.

【0006】[0006]

【課題を解決するための手段】この発明による循環流動
床型焼却炉は、上記の目的を達成するために、流動媒体
粒子を高速流動化させて高速流動床を形成し、この流動
床において被焼却物を燃焼させる主焼却炉と、主焼却炉
から放出される流動媒体粒子を排ガスと分離させて捕集
するサイクロンと、被焼却物投入部を有しかつサイクロ
ンにより捕集された流動媒体粒子の熱により被焼却物を
熱分解させる熱分解炉と、熱分解炉から主焼却炉へ供給
される流動媒体粒子および被焼却物の量を制御する空気
式制御バルブと、被焼却物の熱分解により発生した熱分
解ガスを主焼却炉へ供給する熱分解ガス供給用流路と、
熱分解ガス供給用流路中に設けられた熱分解ガス冷却部
とよりなるものである。
[Means for Solving the Problems] In order to achieve the above object, the circulating fluidized bed incinerator according to the present invention fluidizes fluidized medium particles at high speed to form a high speed fluidized bed, and in this fluidized bed, A main incinerator that burns the incineration material, a cyclone that separates and collects the fluidized medium particles released from the main incinerator from the exhaust gas, and a part that inputs the incinerated material and that collects the fluidized medium particles by the cyclone. A pyrolysis furnace that thermally decomposes the material to be incinerated using the heat of a pyrolysis gas supply channel for supplying the pyrolysis gas generated by the pyrolysis gas to the main incinerator;
It consists of a pyrolysis gas cooling section provided in a pyrolysis gas supply flow path.

【0007】[0007]

【作用】都市ごみ等の被焼却物は、被焼却物投入部より
熱分解炉内に投入されて、流動媒体粒子の熱により熱分
解される。被焼却物の熱分解により発生した熱分解ガス
は、熱分解炉から主焼却炉へ至る熱分解ガス供給用流路
に流入して、途中熱分解ガス冷却部を通過する。熱分解
ガスには、水蒸気、アンモニア、ダイオキシンの発生要
因となる塩素ガス等が含まれており、熱分解ガス冷却部
を通過した熱分解ガスが露点以下まで冷却されると、凝
縮した水に塩素ガスが溶解し、それがアンモニアによっ
て中和され、塩化アンモニウムとなり、その結果、塩素
ガスが除去された熱分解ガスが主焼却炉へ供給される。 他方、熱分解された後の被焼却物は、流動媒体粒子とと
もに、空気式制御バルブを通じて、主焼却炉へ供給され
る。主焼却炉に供給された前記熱分解ガス及び熱分解後
の被焼却物は、流動媒体粒子が高速流動化されて形成せ
られた高速流動床において完全燃焼される。主焼却炉か
ら排出された排ガスと流動媒体粒子とは、サイクロンに
おいて分離され、排ガスはサイクロン外へ排出され、流
動媒体粒子は熱分解炉内へ捕集される。
[Operation] Waste to be incinerated, such as municipal waste, is charged into the pyrolysis furnace from the incineration material input section and is thermally decomposed by the heat of the fluidized medium particles. The pyrolysis gas generated by the pyrolysis of the material to be incinerated flows into the pyrolysis gas supply channel leading from the pyrolysis furnace to the main incinerator, and passes through a pyrolysis gas cooling section on the way. Pyrolysis gas contains water vapor, ammonia, chlorine gas, etc. that cause the generation of dioxins, and when the pyrolysis gas that has passed through the pyrolysis gas cooling section is cooled to below the dew point, chlorine is added to the condensed water. The gas is dissolved and neutralized by ammonia to form ammonium chloride, so that the pyrolysis gas, free of chlorine gas, is fed to the main incinerator. On the other hand, the material to be incinerated after being pyrolyzed is supplied to the main incinerator together with the fluidized medium particles through the pneumatic control valve. The pyrolysis gas and the material to be incinerated after pyrolysis supplied to the main incinerator are completely combusted in a high-speed fluidized bed formed by high-speed fluidization of fluidized medium particles. The exhaust gas discharged from the main incinerator and the fluidized medium particles are separated in a cyclone, the exhaust gas is discharged outside the cyclone, and the fluidized medium particles are collected in the pyrolysis furnace.

【0008】[0008]

【実施例】以下、この発明の実施例を、図面を参照しな
がら説明する。
Embodiments Hereinafter, embodiments of the present invention will be described with reference to the drawings.

【0009】図1に示す循環流動床型焼却炉は、流動媒
体粒子を高速流動化させて高速流動床を形成し、この流
動床において被焼却物を燃焼させる主焼却炉(1) と
、主焼却炉(1) から排出される流動媒体粒子を排ガ
スと分離させて捕集するサイクロン(2) と、被焼却
物投入部(31)を有しかつサイクロン(2) により
捕集された流動媒体粒子の熱により被焼却物を熱分解さ
せる熱分解炉(3) と、熱分解炉(3) から主焼却
炉(1) へ供給される流動媒体粒子および被焼却物の
量を制御する空気式制御バルブ(4) と、被焼却物の
熱分解により熱分解炉(3) から発生した熱分解ガス
を主焼却炉(1) へ供給する熱分解ガス供給用流路(
5) と、熱分解ガス供給用流路(5) 中に設けられ
た熱分解ガス冷却部(6) とよりなる。
The circulating fluidized bed incinerator shown in FIG. 1 includes a main incinerator (1) in which particles of a fluidized medium are fluidized at high speed to form a high-speed fluidized bed, and the material to be incinerated is burned in this fluidized bed. It has a cyclone (2) that separates fluidized media particles discharged from the incinerator (1) from exhaust gas and collects them, and an incineration material input section (31), and the fluidized media collected by the cyclone (2). A pyrolysis furnace (3) that thermally decomposes the materials to be incinerated using the heat of the particles, and a pneumatic type that controls the amount of fluidized medium particles and materials to be incinerated that are supplied from the pyrolysis furnace (3) to the main incinerator (1). A control valve (4) and a pyrolysis gas supply channel (
5) and a pyrolysis gas cooling section (6) provided in the pyrolysis gas supply channel (5).

【0010】熱分解炉(3) に設けられた被焼却物投
入部(31)は、ごみ乾燥機(7) に連通しており、
都市ごみ等の被焼却物は、まず、ごみ乾燥機(7) に
おいて乾燥される。ごみ乾燥機(7) は、回転軸が水
平よりやや傾斜したロータリーキルンであって、被焼却
物は、キルン内壁に沿って移動しながらキルン下部に配
管供給された排ガスの熱により間接的に加熱され、乾燥
される。被焼却物の乾燥により、熱分解ガス冷却部(6
) における熱分解ガスの冷却処理量が減少し、効率的
に冷却処理を行ないうる。また、ごみ乾燥機(7) に
おいて被焼却物の乾燥により発生したガスは、臭気を伴
っているので、この臭気を除去するため二次燃焼用空気
とともに主焼却炉(1) 内に供給されて燃焼される。 なお、ごみ乾燥機(7) は、キルン内にチューブ、ジ
ャケットを併設してもよく、また排ガス加熱以外の加熱
手段を用いてもよい。
[0010] The incineration material input section (31) provided in the pyrolysis furnace (3) communicates with the waste dryer (7).
The materials to be incinerated, such as municipal waste, are first dried in a waste dryer (7). The garbage dryer (7) is a rotary kiln with a rotation axis slightly inclined from horizontal, and the materials to be incinerated are indirectly heated by the heat of exhaust gas piped to the bottom of the kiln while moving along the inner wall of the kiln. , dried. By drying the material to be incinerated, the pyrolysis gas cooling section (6
) The amount of cooling processing of the pyrolysis gas is reduced, and the cooling processing can be performed efficiently. In addition, the gas generated by drying the materials to be incinerated in the garbage dryer (7) has an odor, so it is supplied to the main incinerator (1) together with secondary combustion air to remove this odor. be burned. Note that the waste dryer (7) may include a tube and a jacket inside the kiln, or may use heating means other than exhaust gas heating.

【0011】サイクロン(2) によって熱分解炉(3
) に捕集された燃焼熱を有する流動媒体粒子は、熱分
解炉(3) 下部から導入される空気あるいは排ガス等
によって極低速流動床を形成し、この流動床において被
焼却物投入部(31)より投入された被焼却物が熱分解
される。なお、熱分解炉(3) における流動媒体粒子
の流動化手段としては、排ガス等の低酸素気体を利用す
れば被焼却物の熱分解を効率よく行なえるが、排ガスの
再循環配管等が複雑になる場合には、空気を用いてもよ
い。
The pyrolysis furnace (3) is activated by the cyclone (2).
) The fluidized medium particles having combustion heat collected in the pyrolysis furnace (3) form an extremely low-velocity fluidized bed by air or exhaust gas introduced from the lower part of the pyrolysis furnace (3), and in this fluidized bed, the incinerated material input section (31 ) The materials to be incinerated are thermally decomposed. In addition, as a means of fluidizing the fluidized medium particles in the pyrolysis furnace (3), if low-oxygen gas such as exhaust gas is used, the material to be incinerated can be thermally decomposed efficiently, but the exhaust gas recirculation piping etc. are complicated. If so, air may be used.

【0012】熱分解炉(3) で発生した熱分解ガスは
、主燃焼炉(1)へ至る熱分解ガス供給用流路(5) 
に流入する。熱分解ガス供給用流路(5) は、熱分解
ガスが下降するガス下降部(51)を備えており、ガス
下降部(51)の上部に熱分解ガス冷却部(6) が、
下端部にドレン(52)がそれぞれ設けられている。な
お、熱分解ガス冷却部(6)における冷却手段として、
主焼却炉(1) に導入される燃焼用空気を利用するこ
とにより、燃焼用空気が予熱されて、主焼却炉(1) 
における燃焼効率の向上に寄与できる。熱分解ガス冷却
部(6) において、熱分解ガスが露点以下に冷却され
ると、凝縮した水に塩素ガスが溶解し、それがアンモニ
アによって中和され、塩化アンモニウムとなる。これに
より、塩素が除去された熱分解ガスが主焼却炉(1) 
へ供給され、他方、塩化アンモニウムはガス下降部(5
1)の下端部に設けられたドレン(52)より熱分解ガ
ス供給用流路(5) 外へ排出される。
The pyrolysis gas generated in the pyrolysis furnace (3) is passed through the pyrolysis gas supply channel (5) leading to the main combustion furnace (1).
flows into. The pyrolysis gas supply channel (5) is equipped with a gas descending section (51) through which the pyrolysis gas descends, and a pyrolysis gas cooling section (6) is provided above the gas descending section (51).
A drain (52) is provided at each lower end. In addition, as a cooling means in the pyrolysis gas cooling section (6),
By using the combustion air introduced into the main incinerator (1), the combustion air is preheated and the main incinerator (1) is heated.
This can contribute to improving combustion efficiency. In the pyrolysis gas cooling section (6), when the pyrolysis gas is cooled below its dew point, chlorine gas is dissolved in the condensed water, which is neutralized by ammonia and becomes ammonium chloride. As a result, the pyrolysis gas from which chlorine has been removed is transferred to the main incinerator (1).
while ammonium chloride is supplied to the gas descending section (5
1) is discharged to the outside of the pyrolysis gas supply channel (5) from the drain (52) provided at the lower end.

【0013】主燃焼炉(1) には、炉下部より一次燃
焼用空気が導入されるとともに、炉側部に設けられた二
次燃焼用空気導入部(11)より二次燃焼用空気が導入
される。 また、炉下部には不燃物排出口(12)が設けられて、
被焼却物中の不燃物が流動媒体粒子とともに排出される
ようになされている。不燃物排出口(12)から排出さ
れた不燃物および流動媒体粒子は、振動ふるい等により
ふるい分けられ、流動媒体粒子は熱分解炉(3) 内に
戻される。主焼却炉(1) 内において、二次燃焼用空
気導入部(11)より下方の一次燃焼域では、一次燃焼
用空気の量を制御して若干低速の流動床が形成されてお
り、不燃物排出口(13)から不燃物を排出するのを容
易ならしめている。二次燃焼用空気導入部(11)より
上方の二次燃焼域では、二次燃焼用空気の量を制御して
流動媒体粒子による高速流動床が形成されており、この
高速流動床において、熱分解ガス供給用流路(5) か
ら供給された熱分解ガスと、空気式制御バルブ(4) 
を通じて流動媒体粒子とともに供給された熱分解後の被
焼却物とが完全燃焼される。
[0013] Into the main combustion furnace (1), primary combustion air is introduced from the lower part of the furnace, and secondary combustion air is introduced from the secondary combustion air introduction part (11) provided at the side of the furnace. be done. In addition, a non-combustible material discharge port (12) is provided at the bottom of the furnace.
The incombustible materials in the incineration material are discharged together with the fluidized medium particles. The incombustibles and fluidized medium particles discharged from the incombustibles discharge port (12) are sieved by a vibrating sieve or the like, and the fluidized media particles are returned to the pyrolysis furnace (3). In the primary combustion zone below the secondary combustion air introduction part (11) in the main incinerator (1), a fluidized bed with a slightly low velocity is formed by controlling the amount of primary combustion air, and non-combustible materials are This makes it easy to discharge incombustibles from the discharge port (13). In the secondary combustion zone above the secondary combustion air introduction section (11), a high-speed fluidized bed is formed by fluidized medium particles by controlling the amount of secondary combustion air. The pyrolysis gas supplied from the cracked gas supply channel (5) and the pneumatic control valve (4)
The pyrolyzed incineration material supplied together with the fluidized medium particles is completely combusted through the combustion chamber.

【0014】サイクロン(2) は、上部円筒状部と下
部漏斗状部とよりなりかつ上側部が主燃焼炉(1) の
上側部と連通し、下端部が熱分解炉(3) 内に至るサ
イクロン外筒(21)と、サイクロン外筒(21)の上
部中央に配設されて、その上端部がサイクロン(3) 
の外部に至るサイクロン内筒(22)とを備えている。 主焼却炉(1) から排出された排ガスは、サイクロン
外筒(21)の上部から接線方向に吹込まれ、内部を壁
面に沿って旋回しながら漏斗状下部に入り、次第に中心
部の上昇ガス流に転じてサイクロン内筒(22)から排
出される。他方、流動媒体粒子は、大きな遠心力のため
壁面に衝突し、沈降しながら熱分解炉(4) 内へ捕集
される。
The cyclone (2) consists of an upper cylindrical part and a lower funnel-shaped part, and the upper part communicates with the upper part of the main combustion furnace (1), and the lower end reaches into the pyrolysis furnace (3). The cyclone outer cylinder (21) is arranged at the center of the upper part of the cyclone outer cylinder (21), and the upper end thereof is connected to the cyclone (3).
The cyclone inner cylinder (22) extends to the outside of the cyclone. Exhaust gas discharged from the main incinerator (1) is blown in tangentially from the upper part of the cyclone outer cylinder (21), enters the funnel-shaped lower part while swirling inside the cyclone outer cylinder (21), and gradually rises in the gas flow in the center. It is then discharged from the cyclone inner cylinder (22). On the other hand, the fluidized medium particles collide with the wall surface due to the large centrifugal force, and are collected into the pyrolysis furnace (4) while settling.

【0015】サイクロン(2) から排出された排ガス
は、熱回収部において熱回収されたのち排ガス処理され
あるいは煙道へ導入されるが、うち一部はごみ乾燥機(
7) に供給されて被焼却物の加熱乾燥に利用されたり
、あるいは熱分解炉(4) へ供給されて、流動媒体粒
子の流動化手段として利用される。
[0015] The exhaust gas discharged from the cyclone (2) is heat-recovered in the heat recovery section and then treated with the exhaust gas or introduced into the flue, but some of it is sent to the garbage dryer (
7) and used for heating and drying of the materials to be incinerated, or supplied to the pyrolysis furnace (4) and used as a means for fluidizing fluidized medium particles.

【0016】[0016]

【発明の効果】この発明の循環流動床型焼却炉によれば
、都市ごみ等の被焼却物の焼却が、流動媒体粒子が高速
流動化されて形成せられた高速流動床において行なわれ
るので、高効率燃焼による一酸化炭素の排出量の低減が
可能となり、現状のダイオキシン排出規制に十分に対応
しうる。
[Effects of the Invention] According to the circulating fluidized bed incinerator of the present invention, incineration of materials to be incinerated such as municipal waste is carried out in a high-speed fluidized bed formed by high-speed fluidization of fluidized medium particles. High-efficiency combustion makes it possible to reduce carbon monoxide emissions, making it fully compliant with current dioxin emission regulations.

【0017】また、被焼却物の熱分解により発生した熱
分解ガスが、主焼却炉へ至る熱分解ガス供給用流路中に
設けられた熱分解ガス冷却部を通過して露点以下まで冷
却されることにより、凝縮した水に塩素ガスが溶解し、
それがアンモニアによって中和され、塩化アンモニウム
となり、その結果、塩素ガスが除去された熱分解ガスが
主焼却炉へ供給されるので、特別な脱塩剤(NaOH、
Ca(OH)2 )を用いることなく、塩素を容易に除
去することができる。
[0017] Furthermore, the pyrolysis gas generated by the thermal decomposition of the material to be incinerated passes through a pyrolysis gas cooling section provided in the pyrolysis gas supply flow path leading to the main incinerator, and is cooled to below the dew point. By doing so, chlorine gas is dissolved in the condensed water,
It is neutralized by ammonia to become ammonium chloride, so that the pyrolysis gas from which chlorine gas has been removed is fed to the main incinerator using special desalting agents (NaOH,
Chlorine can be easily removed without using Ca(OH)2).

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

【図1】この発明による循環流動床型焼却炉の1実施例
を示す垂直断面図である。
FIG. 1 is a vertical sectional view showing one embodiment of a circulating fluidized bed incinerator according to the present invention.

【符号の説明】[Explanation of symbols]

1  ……主焼却炉 2  ……サイクロン 3  ……熱分解炉 4  ……空気式制御バルブ 5  ……熱分解ガス供給用流路 6  ……熱分解ガス冷却部 1... Main incinerator 2...Cyclone 3...Pyrolysis furnace 4...Pneumatic control valve 5...Pyrolysis gas supply channel 6...Pyrolysis gas cooling section

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】流動媒体粒子を高速流動化させて高速流動
床を形成し、この流動床において被焼却物を燃焼させる
主焼却炉と、主焼却炉から排出される流動媒体粒子を排
ガスと分離させて捕集するサイクロンと、被焼却物投入
部を有しかつサイクロンにより捕集された流動媒体粒子
の熱により被焼却物を熱分解させる熱分解炉と、熱分解
炉から主焼却炉へ供給される流動媒体粒子および被焼却
物の量を制御する空気式制御バルブと、被焼却物の熱分
解により発生した熱分解ガスを主焼却炉へ供給する熱分
解ガス供給用流路と、熱分解ガス供給用流路中に設けら
れた熱分解ガス冷却部とよりなる循環流動床型焼却炉。
Claim 1: A main incinerator that fluidizes fluidized media particles at high speed to form a high-speed fluidized bed and burns the materials to be incinerated in this fluidized bed, and separates fluidized media particles discharged from the main incinerator from exhaust gas. a cyclone that collects the incinerated material, a pyrolysis furnace that has a part for incinerating the material to be incinerated and thermally decomposes the material to be incinerated by the heat of the fluidized medium particles collected by the cyclone, and a pyrolysis furnace that supplies the material to the main incinerator. a pneumatic control valve that controls the amount of fluidized media particles and incineration materials; a pyrolysis gas supply channel that supplies pyrolysis gas generated by thermal decomposition of the incineration materials to the main incinerator; A circulating fluidized bed incinerator consisting of a pyrolysis gas cooling section provided in a gas supply channel.
JP3124054A 1991-05-28 1991-05-28 Circulating fluidized bed type incinerator Withdrawn JPH04350409A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3124054A JPH04350409A (en) 1991-05-28 1991-05-28 Circulating fluidized bed type incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3124054A JPH04350409A (en) 1991-05-28 1991-05-28 Circulating fluidized bed type incinerator

Publications (1)

Publication Number Publication Date
JPH04350409A true JPH04350409A (en) 1992-12-04

Family

ID=14875833

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3124054A Withdrawn JPH04350409A (en) 1991-05-28 1991-05-28 Circulating fluidized bed type incinerator

Country Status (1)

Country Link
JP (1) JPH04350409A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1998040672A1 (en) * 1997-03-13 1998-09-17 Hitachi Zosen Corporation Combustion device
JP2006292275A (en) * 2005-04-11 2006-10-26 Ishikawajima Harima Heavy Ind Co Ltd Circulating fluidized bed separation combustion method and combustion device using the method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1998040672A1 (en) * 1997-03-13 1998-09-17 Hitachi Zosen Corporation Combustion device
JP2006292275A (en) * 2005-04-11 2006-10-26 Ishikawajima Harima Heavy Ind Co Ltd Circulating fluidized bed separation combustion method and combustion device using the method
JP4553132B2 (en) * 2005-04-11 2010-09-29 株式会社Ihi Combustion apparatus using circulating fluidized bed separation combustion method

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