JPH10205724A - Heating system for thermal decomposition reactor for waste treatment device - Google Patents

Heating system for thermal decomposition reactor for waste treatment device

Info

Publication number
JPH10205724A
JPH10205724A JP9012464A JP1246497A JPH10205724A JP H10205724 A JPH10205724 A JP H10205724A JP 9012464 A JP9012464 A JP 9012464A JP 1246497 A JP1246497 A JP 1246497A JP H10205724 A JPH10205724 A JP H10205724A
Authority
JP
Japan
Prior art keywords
heat storage
heat
gas
temperature
thermal decomposition
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Withdrawn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
JP9012464A
Other languages
Japanese (ja)
Inventor
Kenichi Nagata
健一 永田
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.)
Mitsui Engineering and Shipbuilding Co Ltd
Original Assignee
Mitsui Engineering and Shipbuilding Co 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 Mitsui Engineering and Shipbuilding Co Ltd filed Critical Mitsui Engineering and Shipbuilding Co Ltd
Priority to JP9012464A priority Critical patent/JPH10205724A/en
Publication of JPH10205724A publication Critical patent/JPH10205724A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/34Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery

Landscapes

  • Incineration Of Waste (AREA)
  • Air Supply (AREA)
  • Gasification And Melting Of Waste (AREA)

Abstract

PROBLEM TO BE SOLVED: To easily generate a heating medium, fed to a thermal decomposition reactor, by a low-cost device and to improve thermal efficiency. SOLUTION: In a waste treatment device 1 having a thermal decomposition reactor 5 to effect thermal decomposition of waste (a) by a heating medium, heat storage tanks 24 and 25 charged with a heat storage material are arranged in the vicinity of the thermal decomposition reactor 5. Dry distillation gas G1 is mixed in temperature up air h' discharged from one heat storage tank 24 and by burning the mixture gas, high temperature combustion gas G4 is generated. The combustion gas G4 is supplied as a heating medium to the thermal decomposition reactor 5 and the combustion gas G4 discharged from the thermal decomposition reactor 5 is fed to the other heat storage tank 25, and heat storage material with which the other heat storage tank 25 is charged is heated.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は廃棄物処理装置にお
ける熱分解反応器の加熱方式、より詳しくは廃棄物(家
庭やオフィスなどから出される都市ごみ等の一般廃棄
物、廃プラスチック、カーシュレッダー・ダスト、廃オ
フィス機器、電子機器、化成品等の産業廃棄物など、可
燃物を含むもの)を加熱して熱分解し、乾留ガスと主と
して不揮発性成分よりなる熱分解残留物とを生成し、こ
の乾留ガスと熱分解残留物中の燃焼性成分とを燃焼器に
供給して燃焼処理するようにした廃棄物処理装置におけ
る熱分解反応器の加熱方式に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for heating a pyrolysis reactor in a waste treatment apparatus, and more particularly, to waste (general waste such as municipal waste from homes and offices, waste plastic, car shredders, etc.). Dust, waste office equipment, electronic equipment, industrial wastes such as chemical products, etc., including combustibles) are heated and thermally decomposed to produce dry distillation gas and pyrolysis residues mainly composed of non-volatile components, The present invention relates to a heating method for a pyrolysis reactor in a waste treatment apparatus in which the carbonized gas and the combustible components in the pyrolysis residue are supplied to a combustor for combustion treatment.

【0002】[0002]

【従来の技術】都市ごみ等の一般廃棄物や廃プラスチッ
ク等の可燃物を含む産業廃棄物の処理装置として、例え
ば特公平6−56253号公報に開示されたものが知ら
れている。この廃棄物処理装置は、廃棄物を熱分解反応
器に入れて低酸素雰囲気中で熱媒体である加熱空気によ
って加熱し、乾留ガス(熱分解ガス)と主として不揮発
性成分からなる熱分解残留物とを生成し、この乾留ガス
と熱分解残留物とを排出装置において分離する。更に、
熱分解残留物を冷却した後、分離装置に供給して燃焼性
成分と、例えば金属や陶器、砂利、コンクリート片等の
瓦礫よりなる不燃焼性成分とに分離し、更に前記燃焼性
成分を粉砕し、熱分解カーボンを主体とする燃焼性成分
と前記した乾留ガスとを燃焼溶融炉に導いて燃焼させ、
生じた灰分を燃焼溶融炉の燃焼熱により溶融して溶融ス
ラグとなし、この溶融スラグを外部に排出して冷却固化
させるようにしたものである。
2. Description of the Related Art An apparatus disclosed in, for example, Japanese Patent Publication No. 6-56253 is known as an apparatus for treating general waste such as municipal waste and combustible materials such as waste plastic. This waste treatment equipment puts waste into a pyrolysis reactor, heats it in a low-oxygen atmosphere with heated air as a heat medium, and generates pyrolysis residue consisting mainly of non-volatile components and a dry distillation gas (pyrolysis gas). And the pyrolysis gas and the pyrolysis residue are separated in a discharge device. Furthermore,
After cooling the pyrolysis residue, it is supplied to a separator to separate combustible components and non-combustible components such as rubble such as metals, pottery, gravel and concrete pieces, and further pulverize the combustible components. Then, the combustible component mainly composed of pyrolytic carbon and the above-mentioned dry distillation gas are led to a combustion melting furnace and burned,
The generated ash is melted by the combustion heat of the combustion melting furnace to form molten slag, and the molten slag is discharged to the outside to be cooled and solidified.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、上記熱
分解反応器において、廃棄物を加熱する加熱空気は、燃
焼溶融炉の後流に配置された熱交換器(高温空気加熱
器)により加熱されるが、この熱交換器は、別置として
設けねばならなかった。
However, in the above-mentioned pyrolysis reactor, the heated air for heating the waste is heated by a heat exchanger (high-temperature air heater) arranged downstream of the combustion melting furnace. However, this heat exchanger had to be provided separately.

【0004】また、この熱交換器は、高温の腐蝕性ガス
中に配置されるため耐熱性、耐蝕性が要求され製作コス
トが高くなるとともに、その保守作業が面倒になるとい
う問題があった。
Further, since this heat exchanger is disposed in a high-temperature corrosive gas, heat resistance and corrosion resistance are required, so that the production cost is increased and the maintenance work is troublesome.

【0005】[0005]

【課題を解決するための手段】本発明は前記したような
問題点を解決するためになされたものであって、その第
1の発明は、破棄物を熱分解反応器内に投入し熱媒体に
より加熱して熱分解し、乾留ガスと主として不揮発性成
分よりなる熱分解残留物とを生成し、該乾留ガスと熱分
解残留物とを排出装置において分離し、前記熱分解残留
物を冷却した後燃焼性成分と不燃焼性成分とに分離し、
前記乾留ガスと前記燃焼性成分とを燃焼器に供給して燃
焼処理するようにした廃棄物処理装置において、蓄熱槽
内に装填された蓄熱材を前記熱分解反応器から排出され
る熱媒体により加熱するとともに該加熱された蓄熱材と
常温空気とを接触させて昇温空気となし、該昇温空気に
前記乾留ガスを混合して燃焼し高温の燃焼ガスを生成
し、該燃焼ガスを熱媒体として熱分解反応器に供給して
該熱分解反応器を加熱するようにした廃棄物処理装置に
おける熱分解反応器の加熱方式を提供せんとするもので
ある。
SUMMARY OF THE INVENTION The present invention has been made to solve the above-mentioned problems, and a first invention of the present invention is to throw waste into a pyrolysis reactor and heat the medium. To produce a pyrolysis gas and a pyrolysis residue mainly composed of non-volatile components.The pyrolysis residue was separated from the pyrolysis gas in a discharge device, and the pyrolysis residue was cooled. Separated into post-combustible components and non-combustible components,
In a waste treatment apparatus in which the carbonized gas and the combustible component are supplied to a combustor for combustion treatment, a heat storage material loaded in a heat storage tank is heated by a heat medium discharged from the thermal decomposition reactor. While heating, the heated heat storage material is brought into contact with the room temperature air to form heated air, and the dry distillation gas is mixed with the heated air to burn and generate a high-temperature combustion gas. It is an object of the present invention to provide a heating system for a pyrolysis reactor in a waste treatment apparatus in which the pyrolysis reactor is heated by being supplied to a pyrolysis reactor as a medium.

【0006】そして、実際には蓄熱材を装填した蓄熱槽
は少なくとも2基配置され、一方(一つ)の蓄熱槽から
排出される昇温空気に乾留ガスを混合して燃焼し高温の
燃焼ガスを生成しているとき、他方(残り)の蓄熱槽内
に熱分解反応器から排出される低温の熱媒体(燃焼ガ
ス)が供給され熱回収される。そして所定の時間経過後
において切替ることにより蓄熱槽を繰返し交互に使用し
連続して高温の燃焼ガスを生成し熱分解反応器が加熱さ
れる。そして好ましくは高温の燃焼ガスの温度が検出さ
れ、その結果に基づき乾留ガスの混合量を制御して高温
の燃焼ガスの温度を所定の範囲となるよう制御されるの
である。
In practice, at least two heat storage tanks loaded with a heat storage material are arranged, and a high-temperature combustion gas is produced by mixing a dry distillation gas with heated air discharged from one (one) heat storage tank and burning. Is generated, a low-temperature heat medium (combustion gas) discharged from the pyrolysis reactor is supplied into the other (remaining) heat storage tank, and heat is recovered. By switching after a predetermined time, the heat storage tanks are used alternately and repeatedly to continuously generate high-temperature combustion gas and heat the pyrolysis reactor. Preferably, the temperature of the high-temperature combustion gas is detected, and the mixing amount of the carbonization gas is controlled based on the result to control the temperature of the high-temperature combustion gas to be within a predetermined range.

【0007】第2の発明は、廃棄物を熱分解反応器内に
投入し、熱媒体により大気圧下において加熱して熱分解
し、乾留ガスと主として不揮発性成分よりなる熱分解残
留物とを生成し、該乾留ガスと熱分解残留物とを排出装
置において分離し、前記熱分解残留物を冷却した後燃焼
性成分と不燃焼性成分とに分離し、前記乾留ガスと前記
燃焼性成分とを燃焼器に供給して燃焼処理するようにし
た廃棄物処理装置において、前記熱分解反応器から排出
される熱媒体である空気に前記乾留ガスを混合して燃焼
し高温の燃焼ガスを生成し、該燃焼ガスを蓄熱材が装填
された蓄熱槽に供給して前記蓄熱材を加熱し、該加熱さ
れた蓄熱材と常温空気とを接触させて高温空気を生成
し、該高温空気を熱媒体として熱分解反応器に供給する
ようにした廃棄物処理装置における熱分解反応器の加熱
方式を提供するものである。
In a second aspect of the present invention, the waste is charged into a pyrolysis reactor, and is thermally decomposed by heating at atmospheric pressure with a heat medium to form a pyrolysis gas and a pyrolysis residue mainly composed of non-volatile components. Generated, the pyrolysis gas and the pyrolysis residue are separated in a discharge device, and after cooling the pyrolysis residue, the pyrolysis residue is separated into a combustible component and a non-combustible component. Is supplied to a combustor to perform a combustion treatment, wherein the dry distillation gas is mixed with air serving as a heat medium discharged from the pyrolysis reactor and burned to produce a high-temperature combustion gas. Supplying the combustion gas to a heat storage tank loaded with a heat storage material to heat the heat storage material, bringing the heated heat storage material into contact with room temperature air to generate high temperature air, and transferring the high temperature air to a heat medium. Waste treatment that is supplied to the pyrolysis reactor There is provided a heating method of the pyrolysis reactor in the apparatus.

【0008】そして、この第2の発明においても実際に
は蓄熱槽は少なくとも2基配置され、一方(一つ)の蓄
熱槽で生成された高温空気が熱媒体として熱分解反応器
に供給されているとき、他方(残り)の蓄熱槽には燃焼
ガスが供給され蓄熱材が加熱される。そして所定の時間
経過後において切替ることにより蓄熱槽を繰返し交互に
使用し連続して高温空気を生成し熱分解反応器が加熱さ
れるのである。
In the second invention, at least two heat storage tanks are actually provided, and the high-temperature air generated in one (one) heat storage tank is supplied to the thermal decomposition reactor as a heat medium. When it is, the combustion gas is supplied to the other (remaining) heat storage tank to heat the heat storage material. Then, after a predetermined time has elapsed, the heat storage tanks are repeatedly used alternately by switching to generate high-temperature air continuously to heat the pyrolysis reactor.

【0009】[0009]

【発明の実施の形態】以下本発明による廃棄物処理装置
における熱分解反応器の加熱方式の実施の形態を説明す
る。尚、図1、2において、バブル記号を黒く塗りつぶ
したものは閉を示し、黒く塗りつぶさないものは開を示
す。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of a heating system for a thermal decomposition reactor in a waste treatment apparatus according to the present invention will be described below. In FIGS. 1 and 2, black symbols in a bubble symbol indicate closed, and non-black symbols indicate an open symbol.

【0010】図1は、第1の発明による廃棄物処理装置
における熱分解反応器の加熱方式の一実施の形態を示す
系統図である。廃棄物処理装置1は、都市ごみ等の廃棄
物aを、例えば二軸剪断式等の破砕機で、150mm角
以下に破砕し、コンベア等により投入部2に投入し、ス
クリューフィーダ3を経て熱分解反応器5内に供給す
る。熱分解反応器5内に供給された廃棄物aは、後述す
る方式により300〜600℃に、通常は450℃程度
に加熱され乾留ガスG1と主として不揮発性成分よりな
る熱分解残留物bとが生成され、この乾留ガスG1と熱
分解残留物bとは排出装置6内で分離され、乾留ガスG
1は乾留ガスラインL1を経て燃焼器である溶融炉7のバ
ーナ8に供給される。
FIG. 1 is a system diagram showing an embodiment of a heating system for a pyrolysis reactor in a waste treatment apparatus according to the first invention. The waste treatment apparatus 1 crushes waste a such as municipal solid waste into a 150 mm square or less using a crusher such as a biaxial shearing machine, throws the crushed waste into the loading section 2 by a conveyor or the like, and heats the waste through the screw feeder 3. It is supplied into the decomposition reactor 5. The waste a supplied into the pyrolysis reactor 5 is heated to 300 to 600 ° C., usually to about 450 ° C. by a method described later, and the pyrolysis residue G mainly composed of the dry distillation gas G 1 and the non-volatile components b Is generated, and the carbonized gas G 1 and the pyrolysis residue b are separated in the discharge device 6, and the carbonized gas G
1 is supplied to the burner 8 of the melting furnace 7 is a combustor through a carbonization gas line L 1.

【0011】一方、熱分解残留物bは、冷却装置9に供
給され、ここで酸化の虞れのない温度、例えば80℃程
度まで冷却される。そしてこの冷却された熱分解残留物
bは分離装置10に供給され、主としてカーボンよりな
る燃焼性成分cと金属や瓦礫等の不燃焼性成分dとに分
離され、不燃焼性成分dはコンテナ11に回収されると
ともに燃焼性成分cは粉砕機12により1mm程度まで
粉砕され燃焼性成分ラインL2を経て溶融炉7のバーナ
8に供給され、ここで乾留ガスラインL1を経て供給さ
れた乾留ガスG1と押込送風機13により空気ラインL3
から供給される燃焼用空気eとにより約1、300℃程
度の高温で燃焼され、この燃焼により生じた燃焼灰及び
燃焼性成分c中に含まれている灰分は溶融スラグfとな
って溶融炉7の内壁に付着、流下する。そして下部のス
ラグ排出口14から水槽15内に流下し冷却され固化す
る。
On the other hand, the pyrolysis residue b is supplied to a cooling device 9, where it is cooled to a temperature at which there is no fear of oxidation, for example, about 80 ° C. Then, the cooled pyrolysis residue b is supplied to the separation device 10 and separated into a combustible component c mainly composed of carbon and a non-combustible component d such as metal and rubble. with the recovered combustible components c is supplied to the burner 8 is ground to 1mm approximately by a pulverizer 12 combustible component line L 2 a through molten furnace 7 was supplied here through a carbonization gas line L 1 retorting An air line L 3 is formed by the gas G 1 and the forced blower 13.
Combustion at a high temperature of about 1,300 ° C. with the combustion air e supplied from the furnace, and the combustion ash generated by this combustion and the ash contained in the combustible component c become molten slag f to form a melting slag f. 7 adheres to the inner wall and flows down. Then, it flows down into the water tank 15 from the lower slag discharge port 14 and is cooled and solidified.

【0012】溶融炉7内で発生した高温の燃焼ガスG2
は、排ガスラインL4を経て高温空気加熱器16及び廃
熱ボイラ17で熱回収された後集塵装置18で除塵され
かつガス洗浄装置19で洗浄され比較的低温でクリーン
な排ガスG3となって大部分は煙突20から大気中に放
出され、一部はイナートガスラインL5を経て冷却装置
9に供給されるようになっている。符号21は誘引送風
機であり、符号22は廃熱ボイラ17で発生した蒸気s
により発電される発電装置、符号23はイナートガス供
給用の送風機である。
The high-temperature combustion gas G 2 generated in the melting furnace 7
Is a hot air heater 16 and the heat recovered dust collector 18 after which the dust and clean exhaust gas G 3 at a relatively low temperature and washed with a gas cleaning device 19 in the waste heat boiler 17 via the exhaust gas line L 4 most Te is released from the chimney 20 into the atmosphere, some of which is supplied to the cooling device 9 through the inert gas line L 5. Reference numeral 21 denotes an induction blower, and reference numeral 22 denotes steam s generated in the waste heat boiler 17.
Reference numeral 23 denotes a blower for supplying inert gas.

【0013】次に、符号24は一方の蓄熱槽(以下第1
の蓄熱槽という)であり、符号25は他方の蓄熱槽(以
下第2の蓄熱槽という)であって、この第1の蓄熱槽2
4と第2の蓄熱槽25とは何れも内部に例えばチェッカ
れんがと称する多孔れんがよりなる蓄熱材が装填された
熱交換器として構成され、第1の切換弁26aを有する
第1の空気導入管27と第2の切換弁26bを有する第
2の空気導入管28とにより送風機29と連結されると
ともに第3の切換弁26cを有する第1の低温排ガス管
30と第4の切換弁26dを有する第2の低温排ガス管
31及び排ガス管32により廃熱ボイラ17の後流側の
排ガスラインL4に連通するようになっている。
Next, reference numeral 24 denotes one of the heat storage tanks (hereinafter referred to as a first heat storage tank).
The reference numeral 25 denotes the other heat storage tank (hereinafter referred to as a second heat storage tank), and the first heat storage tank 2
Each of the fourth heat storage tank 25 and the second heat storage tank 25 is configured as a heat exchanger in which a heat storage material made of porous brick called, for example, checker brick is loaded, and a first air introduction pipe having a first switching valve 26a. 27, a first low-temperature exhaust gas pipe 30 having a third switching valve 26c, and a first low-temperature exhaust gas pipe 30 having a third switching valve 26c, and a fourth switching valve 26d connected to a blower 29 by a second air introducing pipe 28 having a second switching valve 26b. The second low-temperature exhaust gas pipe 31 and the second exhaust gas pipe 32 communicate with the exhaust gas line L 4 on the downstream side of the waste heat boiler 17.

【0014】更に、この第1の蓄熱槽24と第2の蓄熱
槽25と熱分解反応器5とは、第5の切換弁26eと第
1の燃焼部33とを有する第1の燃焼ガス供給管34
と、第6の切換弁26fと第2の燃焼部35とを有する
第2の燃焼ガス供給管36とにより、また第7の切換弁
26gを有する第1の高温排ガス管37と第8の切換弁
26hを有する第2の高温排ガス管38とにより連結さ
れている。
Further, the first heat storage tank 24, the second heat storage tank 25, and the thermal decomposition reactor 5 are connected to a first combustion gas supply having a fifth switching valve 26e and a first combustion section 33. Tube 34
And a second high temperature exhaust gas pipe 37 having a seventh switching valve 26g and an eighth switching by a second combustion gas supply pipe 36 having a sixth switching valve 26f and a second combustion section 35. It is connected by a second hot exhaust gas pipe 38 having a valve 26h.

【0015】そして、第1の燃焼ガス供給管34の第1
の燃焼部33の上流側には第9の切換弁26iを有する
第1の乾留ガス供給管39の一端が、また第2の燃焼ガ
ス供給管36の第2の燃焼部35の上流側には第10の
切換弁26jを有する第2の乾留ガス供給管40の一端
が夫々接続されるとともに、この第1の乾留ガス供給管
39及び第2の乾留ガス供給管40の他端は制御弁41
と送風機42とを有する第3の乾留ガス供給管43を経
て乾留ガスラインL1に接続されている。符号44は温
度検出器であって、この温度検出器44の信号V1は、
図示しない制御装置に入力された後、制御信号V2が作
成され制御弁41を制御するようになっている。
The first combustion gas supply pipe 34 has a first
One end of a first carbonization gas supply pipe 39 having a ninth switching valve 26i is provided on the upstream side of the combustion section 33, and on the upstream side of the second combustion section 35 of the second combustion gas supply pipe 36. One end of a second carbonized gas supply pipe 40 having a tenth switching valve 26j is connected to each other, and the other ends of the first carbonized gas supply pipe 39 and the second carbonized gas supply pipe 40 are connected to a control valve 41.
Through the third carbonization gas supply pipe 43 and a blower 42 is connected to the low-temperature carbonization gas line L 1 and. Reference numeral 44 denotes a temperature detector, and the signal V 1 of the temperature detector 44 is
After being input to a control device (not shown), a control signal V 2 is generated to control the control valve 41.

【0016】かかる構成において、今第1の蓄熱槽24
内の蓄熱材が加熱されておりこの蓄熱を利用して熱分解
反応器5を加熱する場合について説明すると、先ず図1
に示すように第1の切換弁26a、第4の切換弁26
d、第5の切換弁26e、第8の切換弁26h及び第9
の切換弁26iを開放し、かつ、第2の切換弁26b、
第3の切換弁26c、第6の切換弁26f、第7の切換
弁26g及び第10の切換弁26jを閉鎖しておく。そ
して、送風機29及び42を起動すると、10〜30℃
程度の新鮮な常温(低温)空気hは、第1の空気導入管
27を経て第1の蓄熱槽24内に供給され熱交換し、1
50〜200℃の昇温空気h’となる。
In such a configuration, the first heat storage tank 24 is
The case where the heat storage material inside is heated and the thermal decomposition reactor 5 is heated using this heat storage will be described.
As shown in the figure, the first switching valve 26a and the fourth switching valve 26
d, the fifth switching valve 26e, the eighth switching valve 26h, and the ninth
, And the second switching valve 26b,
The third switching valve 26c, the sixth switching valve 26f, the seventh switching valve 26g, and the tenth switching valve 26j are closed. Then, when the blowers 29 and 42 are started, 10 to 30 ° C.
The fresh air h at a normal temperature (low temperature) is supplied to the first heat storage tank 24 through the first air introduction pipe 27 and exchanges heat.
The temperature of the heated air h 'becomes 50 to 200C.

【0017】そしてこの昇温空気h’は乾留ガスG1
一部が第1の乾留ガス供給管39から供給され混合ガス
として第1の燃焼部33に導入され燃焼する。そして約
600℃程度の高温の熱媒体としての燃焼ガスG4とな
って第1の燃焼ガス供給管34を経て熱分解反応器5に
供給され、この熱分解反応器5を加熱、即ち熱分解反応
器5内に供給された廃棄物aを加熱し熱分解させる。そ
して、この熱分解反応器5を加熱して200〜250℃
の比較的低温となった熱媒体としての燃焼ガスG4は第
2の高温排ガス管38を経て第2の蓄熱槽25に導入さ
れ、その内部に装填された蓄熱材を加熱し、100℃程
度の低温の燃焼ガスG5となって第2の低温排ガス管3
1及び排ガス管32を経て排ガスラインL4内に供給さ
れる。
[0017] Then the heating air h 'is introduced into the first combustion section 33 as a mixed gas part of the carbonization gas G 1 supplied from the first carbonization gas supply pipe 39 to the combustion. Then, it becomes a combustion gas G 4 as a high-temperature heat medium of about 600 ° C. and is supplied to the pyrolysis reactor 5 through the first combustion gas supply pipe 34, and the pyrolysis reactor 5 is heated, that is, pyrolyzed. The waste a supplied into the reactor 5 is heated and thermally decomposed. Then, the thermal decomposition reactor 5 is heated to 200 to 250 ° C.
The combustion gas G 4 as a relatively low-temperature heat medium is introduced into the second heat storage tank 25 via the second high-temperature exhaust gas pipe 38, and heats the heat storage material loaded therein to about 100 ° C. the second low-temperature exhaust gas pipe 3 becomes the combustion gas G 5 of cold
It is supplied to the exhaust gas line L 4 through 1 and an exhaust gas pipe 32.

【0018】この熱分解反応器5の加熱過程において、
第1の蓄熱槽24内の蓄熱材の温度は低下して来る。こ
の低下の程度を温度検出器44により検知し、制御弁4
1を制御して乾留ガスG1の供給量を増加し、これによ
って燃焼ガスG4を所定の温度に保持することができ
る。そして、所定の時間経過後、各切換弁26a〜26
jを切替えることにより第2の蓄熱槽25により加熱さ
れた昇温空気h’により燃焼ガスG4が生成され、この
燃焼ガスG4により熱分解反応器5は加熱される。勿
論、このとき熱分解反応器5から排出される比較的高温
の燃焼ガスG4は第1の蓄熱槽24に導入され内部に装
填されている蓄熱材を加熱し蓄熱されることにより、蓄
熱槽を繰返し交互に使用し連続して熱分解反応器が加熱
されるのである。
In the heating process of the pyrolysis reactor 5,
The temperature of the heat storage material in the first heat storage tank 24 decreases. The degree of this decrease is detected by the temperature detector 44 and the control valve 4
And controls one to increase the supply amount of the carbonization gas G 1, which makes it possible to retain the combustion gas G 4 to a predetermined temperature. After a lapse of a predetermined time, each of the switching valves 26a to 26
By switching j, the combustion gas G 4 is generated by the heated air h ′ heated by the second heat storage tank 25, and the pyrolysis reactor 5 is heated by the combustion gas G 4 . Of course, at this time, the relatively high-temperature combustion gas G 4 discharged from the pyrolysis reactor 5 is introduced into the first heat storage tank 24 and heats the heat storage material loaded therein to store heat, so that the heat storage tank G 4 is heated. Are used alternately to heat the pyrolysis reactor continuously.

【0019】図2は、第2の発明による廃棄物処理装置
における熱分解反応器の加熱方式の一実施の形態を示す
ものであて、図1と同一符号は同一名称を示す。
FIG. 2 shows an embodiment of a heating system for a pyrolysis reactor in a waste treatment apparatus according to the second invention, and the same reference numerals as in FIG. 1 denote the same names.

【0020】この第2の発明においては第1の燃焼部3
3と第5の切換弁26eとは第1の高温排ガス管45
に、また第2の燃焼部35と第6の切換弁26fとは第
2の高温排ガス管46に夫々配置されている。そして第
7の切換弁26gは第1の高温空気供給管47に、また
第8の切換弁26hは第2の高温空気供給管48に夫々
配置されている。そして先ず、第1の切換弁26a、第
4の切換弁26d、第6の切換弁26f、第7の切換弁
26g及び第10の切換弁26jを開放し、第2の切換
弁26b、第3の切換弁26c、第5の切換弁26e、
第8の切換弁26h及び第9の切換弁26iを閉鎖す
る。
In the second invention, the first combustion section 3
The third and fifth switching valves 26e are connected to the first high-temperature exhaust gas pipe 45.
The second combustion section 35 and the sixth switching valve 26f are arranged in a second high-temperature exhaust gas pipe 46, respectively. The seventh switching valve 26g is disposed on the first high-temperature air supply pipe 47, and the eighth switching valve 26h is disposed on the second high-temperature air supply pipe 48. First, the first switching valve 26a, the fourth switching valve 26d, the sixth switching valve 26f, the seventh switching valve 26g, and the tenth switching valve 26j are opened, and the second switching valve 26b, Switching valve 26c, fifth switching valve 26e,
The eighth switching valve 26h and the ninth switching valve 26i are closed.

【0021】そして送風機29、42を起動することに
より新鮮な常温(低温)空気hは第1の蓄熱槽24内に
供給され、ここで熱交換され600℃程度の高温空気h
1となって第1の高温空気供給管47を経て熱分解反応
器5に供給され、この熱分解反応器5、即ちこの熱分解
反応器5内に投入された廃棄物aを加熱し熱分解させ
る。そして200〜250℃の比較的低温となった加熱
空気h1は、第2の高温排ガス管46を通過する過程に
おいて乾留ガスG1の一部が混合されて第2の燃焼部3
5で燃焼され、例えば600℃程度の高温の燃焼ガスG
6となって第2の蓄熱槽25に導入され内部に装填され
た蓄熱材を加熱する、即ち蓄熱される。
By activating the blowers 29 and 42, fresh normal-temperature (low-temperature) air h is supplied into the first heat storage tank 24, where heat exchange is performed, and high-temperature air h at about 600 ° C.
It becomes 1 and is supplied to the pyrolysis reactor 5 through the first high-temperature air supply pipe 47, and the pyrolysis reactor 5, that is, the waste a charged into the pyrolysis reactor 5, is heated and pyrolyzed. Let it. The heated air h 1 at a relatively low temperature of 200 to 250 ° C. is mixed with a part of the carbonized gas G 1 in the process of passing through the second high-temperature exhaust gas pipe 46, so that the second combustion part 3
5, a combustion gas G having a high temperature of, for example, about 600 ° C.
It becomes 6 and heats the heat storage material introduced into the second heat storage tank 25 and loaded therein, that is, heat is stored.

【0022】そして例えば100〜200℃の低温の燃
焼ガスG7となって第2の低温排ガス管31及び排ガス
管32を経て排ガスラインL4内に供給されるのであ
る。勿論、本実施の形態において、第1の蓄熱槽24内
の温度が低下して来ると、各切換弁26a〜26jを切
換えて、第2の蓄熱槽25により高温加熱空気h1を生
成し、これを熱分解反応器5へ供給し、一方第1の蓄熱
槽24内に燃焼ガスG6を導入して蓄熱材を加熱し蓄熱
することとなる。こうして、蓄熱槽を繰返し交互に使用
し連続して熱分解反応器に投入された廃棄物aを加熱し
熱分解させる。
[0022] The example than is supplied to become a low-temperature combustion gas G 7 of 100 to 200 ° C. The second lower temperature exhaust gas pipe 31 and the exhaust gas line L 4 through the exhaust gas pipe 32. Of course, in this embodiment, when the temperature of the first thermal storage tank 24 is lowered, by switching the respective switching valve 26a-26j, it produces a high-temperature heating air h 1 by the second thermal storage tank 25, This was fed to the pyrolysis reactor 5 while heating the first introduction to the heat storage material to the combustion gas G 6 to the heat storage tank 24 so that the storing heat. In this way, the heat storage tanks are repeatedly used alternately to heat and thermally decompose the waste a which is continuously charged into the thermal decomposition reactor.

【0023】[0023]

【発明の効果】以上の説明から明らかなように、本発明
による廃棄物処理装置における熱分解反応器の加熱方式
によれば、蓄熱槽を用いて熱分解反応器から排出される
熱媒体の熱を回収するようにしたため、熱効率を向上さ
せることができるばかりでなく、乾留ガスの一部を燃焼
させてその熱媒体を所定の温度まで昇温させるようにし
たため、従来のように高温の腐蝕性ガス中に配置された
熱交換器により所定の温度の熱媒体を得る方式に比べて
その製作コストを大幅に低減させることができるという
効果がある。
As is clear from the above description, according to the heating method of the thermal decomposition reactor in the waste treatment apparatus according to the present invention, the heat of the heat medium discharged from the thermal decomposition reactor using the heat storage tank is used. Not only can improve the thermal efficiency, but also burn a part of the carbonization gas to raise the temperature of the heating medium to a predetermined temperature, so that high-temperature corrosive There is an effect that the manufacturing cost can be greatly reduced as compared with a method in which a heat medium of a predetermined temperature is obtained by a heat exchanger disposed in a gas.

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

【図1】第1の発明による廃棄物処理装置における熱分
解反応器の加熱方式の一実施の形態を示す系統図であ
る。
FIG. 1 is a system diagram showing one embodiment of a heating system of a pyrolysis reactor in a waste treatment apparatus according to the first invention.

【図2】第2の発明による廃棄物処理装置における熱分
解反応器の加熱方式の一実施の形態を示す系統図であ
る。
FIG. 2 is a system diagram showing one embodiment of a heating method of a pyrolysis reactor in a waste treatment apparatus according to a second invention.

【符号の説明】[Explanation of symbols]

1 廃棄物処理装置 5 熱分解反応器 6 排出装置 7 溶融炉(燃焼器) 24 第1の蓄熱槽(一方の蓄熱槽) 25 第2の蓄熱槽(他方の蓄熱槽) G1 乾流ガス G4、G6 燃焼ガス a 廃棄物 b 熱分解残留物 c 燃焼性成分 d 不燃焼性成分 h 常温(低温)空気 h’ 昇温空気 h1 空気の熱媒体DESCRIPTION OF SYMBOLS 1 Waste treatment apparatus 5 Thermal decomposition reactor 6 Discharge apparatus 7 Melting furnace (combustor) 24 1st heat storage tank (one heat storage tank) 25 2nd heat storage tank (the other heat storage tank) G 1 Dry flow gas G 4, G 6 combustion gas a waste b pyrolysis residue c combustible component d unburned component h room temperature (cold) air h 'warm air h 1 air heat medium

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI F23G 7/00 F23G 7/00 F23L 15/02 F23L 15/02 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification code FI F23G 7/00 F23G 7/00 F23L 15/02 F23L 15/02

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 廃棄物を熱分解反応器内に投入し熱媒体
により加熱して熱分解し乾留ガスと主として不揮発性成
分よりなる熱分解残留物とを生成し、該乾留ガスと熱分
解残留物とを排出装置において分離し、前記熱分解残留
物を冷却した後燃焼性成分と不燃焼性成分とに分離し、
前記乾留ガスと前記燃焼性成分とを燃焼器に供給して燃
焼処理するようにした廃棄物処理装置において、蓄熱槽
内に装填された蓄熱材を前記熱分解反応器から排出され
る比較的低温の熱媒体により加熱するとともに、該加熱
された蓄熱材と常温空気とを接触させて昇温空気とな
し、該昇温空気に前記乾留ガスを混合して燃焼し高温の
燃焼ガスを生成し、該燃焼ガスを熱媒体として熱分解反
応器に供給し該熱分解反応器を加熱するようにしたこと
を特徴とする廃棄物処理装置における熱分解反応器の加
熱方式。
1. A waste material is introduced into a pyrolysis reactor, heated by a heating medium, and thermally decomposed to produce a dry distillation gas and a pyrolysis residue mainly composed of non-volatile components. Separated in a discharge device, and separated into a combustible component and a non-combustible component after cooling the pyrolysis residue,
In a waste treatment apparatus in which the carbonized gas and the combustible component are supplied to a combustor for combustion treatment, a heat storage material loaded in a heat storage tank is discharged at a relatively low temperature discharged from the thermal decomposition reactor. While heating with the heat medium, the heated heat storage material and room temperature air are brought into contact with each other to form heated air, and the heated air is mixed with the dry distillation gas and burned to generate a high-temperature combustion gas, A method of heating a pyrolysis reactor in a waste treatment apparatus, wherein the combustion gas is supplied to a pyrolysis reactor as a heat medium to heat the pyrolysis reactor.
【請求項2】 熱分解反応器近傍に蓄熱材が装填された
蓄熱槽を少なくとも2基配置し、一方の蓄熱槽から排出
される昇温空気に乾留ガスを混合して燃焼して高温の燃
焼ガスを生成し、該燃焼ガスを熱媒体として熱分解反応
器に供給するとともに、熱分解反応器から排出される熱
媒体である燃焼ガスを他の蓄熱槽に供給し、該他の蓄熱
槽に装填された蓄熱材を加熱するようにした蓄熱槽を繰
返し交互に使用する請求項1記載の廃棄物処理装置にお
ける熱分解反応器の加熱方式。
2. At least two heat storage tanks loaded with a heat storage material are disposed in the vicinity of a thermal decomposition reactor, and a high-temperature combustion is performed by mixing a dry distillation gas with heated air discharged from one of the heat storage tanks and burning. A gas is generated, and the combustion gas is supplied to the thermal decomposition reactor as a heat medium, and the combustion gas, which is a heat medium discharged from the thermal decomposition reactor, is supplied to another heat storage tank, and is supplied to the other heat storage tank. 2. A heating method for a thermal decomposition reactor in a waste treatment apparatus according to claim 1, wherein heat storage tanks for heating the loaded heat storage material are repeatedly and alternately used.
【請求項3】 高温の燃焼ガスの温度を検出して昇温空
気に混合される乾留ガスの量を制御するようにした請求
項1又は2記載の廃棄物処理装置における熱分解反応器
の加熱方式。
3. The heating of a pyrolysis reactor in a waste treatment apparatus according to claim 1, wherein the amount of the dry distillation gas mixed with the heated air is controlled by detecting the temperature of the high-temperature combustion gas. method.
【請求項4】 廃棄物を熱分解反応器内に投入し、熱媒
体により加熱して熱分解し、乾留ガスと主として不揮発
性成分よりなる熱分解残留物とを生成し、該乾留ガスと
熱分解残留物とを排出装置において分離し、前記熱分解
残留物を冷却した後燃焼性成分と不燃焼性成分とに分離
し、前記乾留ガスと前記燃焼性成分とを燃焼器に供給し
て燃焼処理するようにした廃棄物処理装置において、前
記熱分解反応器から排出される熱媒体である空気に前記
乾留ガスを混合して燃焼し高温の燃焼ガスを生成し、該
燃焼ガスを蓄熱材が装填された蓄熱槽に供給して前記蓄
熱材を加熱し、該加熱された蓄熱材と空気とを接触させ
て高温空気を生成し、該高温空気を熱媒体として熱分解
反応器に供給するようにしたことを特徴とする廃棄物処
理装置における熱分解反応器の加熱方式。
4. The waste is put into a pyrolysis reactor, and is thermally decomposed by heating with a heating medium to produce a dry distillation gas and a pyrolysis residue mainly composed of non-volatile components. The pyrolysis residue is separated in a discharge device, the pyrolysis residue is cooled and then separated into a combustible component and a non-combustible component, and the dry distillation gas and the combustible component are supplied to a combustor for combustion. In the waste treatment apparatus that is to be treated, the dry distillation gas is mixed with air serving as a heat medium discharged from the pyrolysis reactor and burned to generate a high-temperature combustion gas, and the heat storage material stores the combustion gas. The heat storage material is supplied to the loaded heat storage tank to heat the heat storage material, the heated heat storage material is brought into contact with air to generate high-temperature air, and the high-temperature air is supplied to the thermal decomposition reactor as a heat medium. Heat in waste treatment equipment characterized in that Heating method for de-reactor.
【請求項5】 熱分解反応器近傍に蓄熱材が装填された
蓄熱槽を少なくとも2基配置し、一方の蓄熱槽で加熱さ
れた高温空気を熱媒体として熱分解反応器に供給すると
ともに、熱分解反応器から排出される低温の熱媒体とし
ての空気に乾留ガスを混合して燃焼させ高温の燃焼ガス
を生成し、該燃焼ガスを他の蓄熱槽へ供給して蓄熱材を
加熱するようにした蓄熱槽を繰返し交互に使用する請求
項4記載の廃棄物処理装置における熱分解反応器の加熱
方式。
5. At least two heat storage tanks loaded with a heat storage material are disposed in the vicinity of the thermal decomposition reactor, and high-temperature air heated in one of the heat storage tanks is supplied to the thermal decomposition reactor as a heat medium, A dry distillation gas is mixed with air as a low-temperature heat medium discharged from the cracking reactor and burned to generate a high-temperature combustion gas, and the combustion gas is supplied to another heat storage tank to heat the heat storage material. 5. A heating method for a thermal decomposition reactor in a waste treatment apparatus according to claim 4, wherein the heat storage tanks are repeatedly and alternately used.
JP9012464A 1997-01-27 1997-01-27 Heating system for thermal decomposition reactor for waste treatment device Withdrawn JPH10205724A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9012464A JPH10205724A (en) 1997-01-27 1997-01-27 Heating system for thermal decomposition reactor for waste treatment device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9012464A JPH10205724A (en) 1997-01-27 1997-01-27 Heating system for thermal decomposition reactor for waste treatment device

Publications (1)

Publication Number Publication Date
JPH10205724A true JPH10205724A (en) 1998-08-04

Family

ID=11806092

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9012464A Withdrawn JPH10205724A (en) 1997-01-27 1997-01-27 Heating system for thermal decomposition reactor for waste treatment device

Country Status (1)

Country Link
JP (1) JPH10205724A (en)

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