JP2002081623A - Pyrolytic gasification melting furnace for waste - Google Patents

Pyrolytic gasification melting furnace for waste

Info

Publication number
JP2002081623A
JP2002081623A JP2000273609A JP2000273609A JP2002081623A JP 2002081623 A JP2002081623 A JP 2002081623A JP 2000273609 A JP2000273609 A JP 2000273609A JP 2000273609 A JP2000273609 A JP 2000273609A JP 2002081623 A JP2002081623 A JP 2002081623A
Authority
JP
Japan
Prior art keywords
section
melting
combustion
pyrolysis
furnace
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2000273609A
Other languages
Japanese (ja)
Inventor
Yuji Mizukoshi
裕治 水越
Yoshiyuki Takii
芳幸 滝井
Megumi Masui
芽 増井
Shuei Kinoshita
秀英 木下
Kenji Ikeda
健治 池田
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.)
ACTREE Corp
Original Assignee
ACTREE 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 ACTREE Corp filed Critical ACTREE Corp
Priority to JP2000273609A priority Critical patent/JP2002081623A/en
Publication of JP2002081623A publication Critical patent/JP2002081623A/en
Pending legal-status Critical Current

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  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)
  • Vertical, Hearth, Or Arc Furnaces (AREA)

Abstract

PROBLEM TO BE SOLVED: To obtain a small sized pyrolytic gasification melting furnace for waste, in which an operation control is easy, troubles in operation caused by tar and ash content are precluded, and harmful substances are not generated. SOLUTION: This furnace is equipped with a pyrolysis section for heating waste under a reductive atmosphere, a combustion section for burning a combustible gas generated by pyrolysis, and a melting section for melting residual solids in an integral furnace body as a continuous space. A dropping part in the pyrolysis section communicates with the top of the combustion section. The combustion section is constituted as a vertically long space to conduct by gravity-dropping the residual solid matter from the pyrolysis section to the melting section. In the melting section, a furnace space is formed nearly horizontally having an inclined bottom surface continuing to the lower end of the combustion section. A hole for dropping melts is provided in the furnace bottom.

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】この発明は、廃棄物を熱分解
して得られる可燃性ガスを利用して当該廃棄物を高温で
焼却する熱分解ガス化溶融炉に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a pyrolysis gasification and melting furnace for incinerating waste at a high temperature using a combustible gas obtained by pyrolyzing waste.

【0002】この発明の特徴は、破砕した廃棄物を間接
加熱方式で還元熱分解して炭化し、その炭化物と熱分解
時に得られる可燃ガスを同伴させて下部燃焼室で燃焼
し、最終工程の溶融エネルギーとして利用することにあ
る。炉の構造としては、還元式熱分解炉とその燃焼炉及
び溶融炉を一体化したことで、ガス化溶融炉の構造を根
底から変えるものである。この構造により、自己発熱量
で溶融完了まで行なうべく、熱量を高効率で利用でき
る。更に、従来構造では分解ガスが冷えてタール化する
ことによる閉鎖事故がまれに発生するが、その事故防止
を可能にする。
A feature of the present invention is that crushed waste is reduced and pyrolyzed by an indirect heating method to be carbonized, and is burned in a lower combustion chamber together with the carbonized material and a combustible gas obtained at the time of pyrolysis. It is to utilize as melting energy. As the furnace structure, the structure of the gasification and melting furnace is fundamentally changed by integrating the reduction-type pyrolysis furnace with its combustion furnace and melting furnace. With this structure, the amount of heat can be used with high efficiency in order to complete the melting with the self-generated heat. Further, in the conventional structure, although a closed accident rarely occurs due to the decomposition gas being cooled and becoming tar, the accident can be prevented.

【0003】[0003]

【従来の技術】従来から廃棄物処理は燃焼と埋立てに頼
っている。通常の焼却炉による燃焼の場合は、非常に多
くの二次燃焼空気を必要とし、燃焼炉の底部に残る主灰
と燃焼ガスに乗って排出される飛灰とについての灰の処
理が必要である。安全な環境の確保の点から、燃焼ガス
及び灰中に含まれるダイオキシンを除去する必要があ
る。そこで従来は、燃焼により生ずるダイオキシンを灰
の中に落として薬品で中和処理するか、コンクリートに
封じ込めるか、キレートと呼ばれる有機化合物で固定化
するという手段が取られている。
2. Description of the Related Art Conventionally, waste disposal relies on combustion and landfill. In the case of combustion using a normal incinerator, a large amount of secondary combustion air is required, and it is necessary to treat ash from the main ash remaining at the bottom of the combustion furnace and fly ash discharged on the combustion gas. is there. From the viewpoint of ensuring a safe environment, it is necessary to remove dioxins contained in combustion gas and ash. Therefore, conventionally, measures have been taken in which dioxin generated by combustion is dropped into ash and neutralized with a chemical, sealed in concrete, or immobilized with an organic compound called a chelate.

【0004】近時、排プラスチックや木材などの可燃有
機物物を300〜500度(摂氏、以下同じ)位の温度
で空気を入れずに乾留して一酸化炭素やメタンガスなど
の可燃ガスとして燃やし、分解しないで残った固形物
は、上記可燃ガスを燃やして得た1400度前後のダイ
オキシンが合成されない高温で溶かして水で急冷してス
ラグ化するという処理が行われており、この種の処理を
行なう焼却炉をガス化溶融炉と称している。
Recently, combustible organic substances such as waste plastics and wood are carbonized at a temperature of about 300 to 500 degrees Celsius (Centigrade, the same applies hereinafter) without air and burnt as combustible gases such as carbon monoxide and methane gas. Solids remaining without decomposition are subjected to a process of melting at a high temperature at which dioxin around 1400 degrees obtained by burning the combustible gas is not synthesized, and rapidly cooling with water to form slag. The incinerator to be performed is called a gasification and melting furnace.

【0005】この場合の燃焼ガスは、従来と同様な方
法、すなわちダイオキシンが再合成される300〜45
0度の温度範囲を急冷処理することにより、ダイオキシ
ンの排出を防止できる。燃焼ではなく溶融を行うのは、
灰を減容化できるという長所があるからで、単なる燃焼
では固形物が10%ほど残るのに対し、溶融すれば灰の
中の空隙がなくなるために、30%程度まで減容でき、
燃焼する際に供給する空気の量も少ないので、燃焼ガス
の量も少なくできるという長所がある。
[0005] The combustion gas in this case is produced in the same manner as in the prior art, that is, 300 to 45 in which dioxin is resynthesized.
By quenching the temperature range of 0 degrees, the emission of dioxin can be prevented. Melting, not burning,
Ash has the advantage of being able to reduce the volume, and mere combustion leaves about 10% of solids, but if it melts, voids in the ash disappear, so it can be reduced to about 30%.
Since the amount of air supplied during combustion is small, there is an advantage that the amount of combustion gas can be reduced.

【0006】[0006]

【発明が解決しようとする課題】しかし従来のガス化溶
融炉は、家庭用の一般廃棄物の処理に用いられ、産業廃
棄物の処理にはあまり利用されていない。その理由は、
産業廃棄物は組成が一定しないことと、処理装置の管理
に不安があるためで、特に産業廃棄物に対する小規模な
ガス化溶融炉は、ほとんど実用化されていないのが現状
である。
However, conventional gasification and melting furnaces are used for the treatment of household general waste, and are not widely used for the treatment of industrial waste. The reason is,
Industrial wastes are not uniform in composition and there is concern about the management of processing equipment. In particular, small-scale gasification and melting furnaces for industrial wastes have hardly been put into practical use.

【0007】さらに従来のガス化溶融炉は、熱分解炉で
生成した可燃ガスに空気を吹き込んでバーナーのように
急激に燃焼させるというのが主流であり、ガス化した後
の残った固形物に対して金属分離を行い、その残りを溶
融炉に入れるという処理を行っている。
[0007] Further, in the conventional gasification and melting furnace, the mainstream is that air is blown into a combustible gas generated in a pyrolysis furnace and burned rapidly like a burner, and solid matter remaining after gasification is removed. On the other hand, metal separation is performed, and the remainder is put into a melting furnace.

【0008】しかし上記の装置では、熱分解炉から燃焼
炉に熱分解ガスを送る流路にガス中のタールが付着して
流路を閉塞させるという問題がある。そこで流路に付着
したタールを掻き取るスクリューを設けるなどしてお
り、装置の維持管理が非常に大変であるという問題があ
る。
However, in the above-mentioned apparatus, there is a problem that tar in the gas adheres to the flow path for sending the pyrolysis gas from the pyrolysis furnace to the combustion furnace, thereby blocking the flow path. Therefore, a screw for scraping tar adhering to the flow path is provided, and there is a problem that maintenance of the apparatus is very difficult.

【0009】そこでこの発明は、主として産業廃棄物の
処理を目的とした熱分解ガス化溶融炉を得ることを課題
としており、運転管理が比較的容易で、燃焼時に生ずる
タールや灰分による運転上のトラブルや有害物質の発生
の危険がなく、かつ装置を比較的小型にすることが可能
な廃棄物の熱分解ガス化溶融炉を得ることを課題として
いる。
Accordingly, an object of the present invention is to obtain a pyrolysis gasification and melting furnace mainly for the treatment of industrial wastes, which is relatively easy to operate and manage, and which is difficult to operate due to tar and ash generated during combustion. It is an object of the present invention to provide a waste pyrolysis gasification and melting furnace which does not have a risk of generating troubles and harmful substances and which can make the apparatus relatively small.

【0010】[0010]

【課題を解決するための手段】この出願の発明に係る熱
分解ガス化溶融炉は、上部の熱分解部と下部の溶融部と
の間に燃焼部を設け、固形分を重力落下により熱分解ガ
スと共に燃焼部及び溶融部に移送し、固形物を分離しな
いで燃焼部で燃焼し、更にその下方の溶融部で溶融する
ことが最大の特徴である。
The pyrolysis gasification and melting furnace according to the present invention has a combustion section between an upper pyrolysis section and a lower melting section, and pyrolyzes solids by gravity. The greatest feature is that the solids are transferred to the combustion section and the melting section together with the gas, burned in the combustion section without separating solids, and further melted in the melting section below.

【0011】この発明の熱分解ガス化溶融炉1は、還元
性雰囲気下で材料(廃棄物)を加熱する熱分解部2と、
この熱分解により生じた可燃性ガスを燃焼する燃焼部3
と、残存した固形物を溶融する溶融部4とを一体の炉体
内に連続する空間として備えている。熱分解部2は燃焼
部3の上方に位置し、燃焼部3は溶融部4の上方に位置
している。熱分解部2は、材料を略水平方向に移送する
移送手段22と輻射加熱手段24と材料の定量フィーダ
21とを備え、定量フィーダ21の反対の側に材料の落
下口11が設けられて、この落下口11が燃焼部3の頂
部に連通している。
The pyrolysis gasification and melting furnace 1 of the present invention comprises a pyrolysis section 2 for heating a material (waste) under a reducing atmosphere;
Combustion unit 3 that burns combustible gas generated by this thermal decomposition
And a melting part 4 for melting the remaining solid matter are provided as a continuous space in an integrated furnace. The pyrolysis section 2 is located above the combustion section 3, and the combustion section 3 is located above the melting section 4. The pyrolysis section 2 includes a transfer means 22 for transferring the material in a substantially horizontal direction, a radiant heating means 24, and a fixed quantity feeder 21 for the material, and a drop port 11 for the material is provided on the opposite side of the fixed quantity feeder 21, The falling port 11 communicates with the top of the combustion section 3.

【0012】燃焼部3は、重力落下により熱分解部2か
らの残存固形物を溶融部4に導く上下方向に長い炉内空
間を形成しており、炉壁には燃焼空気の供給口33が設
けられている。溶融部4は、燃焼部3の下端に連なる底
面が傾斜した略水平方向の炉内空間を形成しており、下
流側の底部に溶融物の落下口と側方に燃焼ガスを吸引す
る排気口13が設けられている。また、この溶融部には
加熱バーナ41が設けられ、必要により前記燃焼部3に
補助加熱バーナ32が設けられる。
The combustion section 3 forms a vertically long furnace space for guiding the remaining solid matter from the pyrolysis section 2 to the melting section 4 by gravity drop, and a combustion air supply port 33 is formed in the furnace wall. Is provided. The melting portion 4 forms a substantially horizontal furnace space in which the bottom surface connected to the lower end of the combustion portion 3 is inclined, and has an outlet for the molten material at the bottom on the downstream side and an exhaust port for sucking the combustion gas to the side. 13 are provided. Further, a heating burner 41 is provided in the melting portion, and an auxiliary heating burner 32 is provided in the combustion portion 3 as necessary.

【0013】溶融部の排出口12の下部には、冷却槽5
0と排出コンベア51とが設けられる。排気口13から
排出されたガスは、熱交換機8、ダイオキシンが再合成
される温度範囲(通常300℃〜450℃)を急冷させ
る減温機6及びマルチサイクロンやバグフィルターなど
の集塵機7を経て大気放出される。この排ガス通路には
排気ファン90が設けられて、燃焼部3に吹込まれた燃
焼空気を積極的に排気口13へと吸引している。
In the lower part of the outlet 12 of the melting part, a cooling tank 5 is provided.
0 and a discharge conveyor 51 are provided. The gas discharged from the exhaust port 13 passes through a heat exchanger 8, a cooler 6 for rapidly cooling the temperature range in which dioxin is resynthesized (usually 300 ° C. to 450 ° C.), and a dust collector 7 such as a multicyclone or a bag filter, and is then discharged to the atmosphere. Released. An exhaust fan 90 is provided in the exhaust gas passage, and actively sucks the combustion air blown into the combustion section 3 to the exhaust port 13.

【0014】この出願の発明の熱分解ガス化溶融炉で
は、定量フィーダ21によって供給された材料が熱分解
部2で輻射加熱手段24の輻射熱により熱分解される。
熱分解された可燃ガスと残存固形物とは、分離されるこ
となく燃焼部3に移送される。燃焼部においては、燃焼
空気が吹込まれることによって、熱分解炉で発生した可
燃ガスが燃焼され、その中を落下して行く固形物を更に
加熱する。
In the pyrolysis gasification and melting furnace of the present invention, the material supplied by the quantitative feeder 21 is pyrolyzed by the radiant heat of the radiant heating means 24 in the pyrolysis section 2.
The pyrolyzed combustible gas and the remaining solid matter are transferred to the combustion unit 3 without being separated. In the combustion section, the combustible gas generated in the pyrolysis furnace is burned by blowing the combustion air, and the solids falling through the combustible gas are further heated.

【0015】溶融部に設けた加熱バーナ41は、溶融部
4の温度を高温に維持して、燃焼部3から落下してきた
固形物を溶融し、排出口12から落下排出させる。燃焼
部3では、可燃ガスを残存固形物と分離しないで、比較
的大面積の炉内空間で燃焼するため、燃焼温度が従来の
熱分解ガス化溶融炉より低くなるので、その分を溶融部
に設けた加熱バーナ41で昇温して、固形物を溶融温度
にまで昇温させる。残存固形物中に含まれる金属は、比
重差と表面張力とによって溶融部4で分離された状態と
なり、これを冷却槽50で冷却することにより、純度の
高い金属が分離されて排出される。従って、排出された
固形物を重力選鉱や磁気選鉱によって分別することによ
り、スラグ中の金属を分離できる。
The heating burner 41 provided in the melting section keeps the temperature of the melting section 4 at a high temperature, melts the solids dropped from the combustion section 3, and drops and discharges the solids from the discharge port 12. In the combustion section 3, the combustible gas is not separated from the residual solids and is burned in a relatively large-area furnace space. Therefore, the combustion temperature is lower than that of the conventional pyrolysis gasification and melting furnace. The temperature is raised by the heating burner 41 provided in the above, and the solid is heated to the melting temperature. The metal contained in the remaining solid matter is separated in the melting part 4 due to the difference in specific gravity and the surface tension. By cooling this in the cooling tank 50, the metal with high purity is separated and discharged. Therefore, the metals in the slag can be separated by separating the discharged solid by gravity separation or magnetic separation.

【0016】ダイオキシンの発生が非常に少なく、主灰
及び飛灰の処理が不要となり、固形排出物もアスファル
トの骨材などとしてリサイクルが可能であり、廃棄物中
の金属も高い純度で分離できる。
The generation of dioxin is extremely low, the treatment of main ash and fly ash is not required, solid waste can be recycled as asphalt aggregate, etc., and metals in waste can be separated with high purity.

【0017】[0017]

【発明の実施の形態】図1はこの出願の発明の一実施形
態を示すブロック図である。この出願の発明に係る熱分
解ガス化溶融炉1は、略水平方向の炉内空間を形成する
熱分解部2と、頂部が熱分解部に連通し、下部が溶融炉
に連通している上下方向の炉内空間を形成する燃焼部3
と、底面が傾斜し略水平方向の炉内空間を形成する溶融
部4とを備えた一体の炉体によって形成される。図示実
施例の熱分解部2は、スクリュコンベアを備えた定量フ
ィーダ21と、若干傾斜した回転胴(回転キルン)22
と、加熱炉23の燃焼ガスを通過させるパイプを炉内空
間に配置することにより形成した加熱パイプ24とを備
えている。定量フィーダ21によって熱分解部2に投入
された廃棄物は、傾斜した回転胴22の回転に伴って攪
拌されつつ反フィーダ側へと移送され、その間に加熱パ
イプ24からの輻射熱によって加熱されて、還元雰囲気
下で還流される。還流により生じた可燃性ガスは、定量
フィーダ21の反対側底部に設けられた落下口11から
下方へと流れて燃焼部3に流入する。また、回転胴22
の回転により落下口11側へと移送された残存固形物も
重力落下により燃焼部3へと落下する。なお、加熱パイ
プ24を通過した加熱炉23の燃焼ガスは、熱分解ガス
化溶融炉の排気と合流して、減温機6、集塵機7を通っ
て大気排出される。加熱炉23の燃料としては重油を用
いているが、熱分解ガス化溶融炉1の排ガスを加熱パイ
プ24に供給することもできる。
FIG. 1 is a block diagram showing an embodiment of the present invention. A pyrolysis gasification and melting furnace 1 according to the invention of this application includes a pyrolysis section 2 forming a furnace space in a substantially horizontal direction, and a vertical section having a top section communicating with the pyrolysis section and a lower section communicating with the melting furnace. Combustion unit 3 that forms a space inside the furnace
And a melting part 4 having a bottom inclined and forming a substantially horizontal furnace space. The pyrolysis section 2 of the illustrated embodiment includes a fixed-quantity feeder 21 having a screw conveyor and a slightly inclined rotating drum (rotating kiln) 22.
And a heating pipe 24 formed by arranging a pipe for passing the combustion gas of the heating furnace 23 in the furnace space. The waste put into the thermal decomposition section 2 by the fixed amount feeder 21 is transferred to the anti-feeder side while being stirred with the rotation of the inclined rotating drum 22, and is heated by radiant heat from the heating pipe 24 during that time. Reflux under reducing atmosphere. The flammable gas generated by the reflux flows downward from the drop port 11 provided on the opposite bottom of the fixed-quantity feeder 21 and flows into the combustion unit 3. Also, the rotating drum 22
The remaining solids transferred to the drop port 11 side by the rotation of also fall into the combustion part 3 by gravity drop. Note that the combustion gas of the heating furnace 23 that has passed through the heating pipe 24 joins the exhaust gas of the pyrolysis gasification and melting furnace, and is discharged to the atmosphere through the desuperheater 6 and the dust collector 7. Although heavy oil is used as the fuel for the heating furnace 23, the exhaust gas of the pyrolysis gasification and melting furnace 1 can be supplied to the heating pipe 24.

【0018】燃焼部3の炉壁には、多数の燃焼空気の供
給口33が設けられ、燃焼空気用ファン31の排気を熱
交換機8で昇温して吹込んでいる。燃焼部3の上部に
は、補助加熱バーナ32が設けられて可燃性ガスに着火
し、炉壁から吹込まれる燃焼空気によって燃焼する。こ
の燃焼部を重量落下して行く固形物は、この燃焼によっ
て加熱されて、燃焼部の下方の溶融部4へと導かれる。
溶融部4では、落下した固形物が加熱バーナ41で更に
加熱されて溶融し、底面の傾斜に従って下流側へと流れ
て、堰42を越えたものが排出口12から冷却槽50内
へと落下する。溶融した固形物は、比重及び表面張力に
よって金属と灰分とが分離され、金属相互もその比重差
によって分別されて冷却槽50へと落下して行くので、
高精度で金属の分離を行なうことができる。図示実施例
の冷却槽では、水冷却が行われて、急冷によりスラグが
破砕されて、排出コンベア51によりスラグ溜め52へ
と搬送される。分離した金属を選鉱するときは、排出コ
ンベア51とスラグ溜め52との間に重力選鉱機や磁気
選鉱機を配置する。
A large number of combustion air supply ports 33 are provided in the furnace wall of the combustion section 3, and the exhaust of a combustion air fan 31 is heated by a heat exchanger 8 and blown. An auxiliary heating burner 32 is provided above the combustion unit 3 to ignite the combustible gas and burn with the combustion air blown from the furnace wall. The solids falling by weight in the combustion section are heated by the combustion and guided to the melting section 4 below the combustion section.
In the melting part 4, the solid matter that has fallen is further heated and melted by the heating burner 41, flows downstream according to the inclination of the bottom surface, and the solid matter that has passed the weir 42 falls from the outlet 12 into the cooling tank 50. I do. The molten solid is separated into metal and ash by specific gravity and surface tension, and the metals are separated by the difference in specific gravity and fall into the cooling tank 50.
Metal can be separated with high accuracy. In the cooling tank of the illustrated embodiment, water cooling is performed, slag is crushed by rapid cooling, and is transported to the slag reservoir 52 by the discharge conveyor 51. When separating the separated metals, a gravity separator or a magnetic separator is arranged between the discharge conveyor 51 and the slag reservoir 52.

【0019】排出口12の側方には排気口13が開口し
ており、この排気口は排気ファン90によって負圧にさ
れており、燃焼部3で炉内に吹込まれている燃焼空気を
積極的に吸引している。この積極的な吸引と熱分解部2
で生成するガスにより、燃焼部の燃焼空気が熱分解部2
に流れるのが阻止される。排気口13から流出した高温
のガスは、熱交換機8で燃焼空気を加熱するのに用いら
れた後、前述した加熱炉の排気と合流して、減温機6及
び集塵機7を通って、煙突91から大気放出される。
An exhaust port 13 is opened to the side of the exhaust port 12, and this exhaust port is set to a negative pressure by an exhaust fan 90, and the combustion section 3 actively promotes the combustion air blown into the furnace. It is sucking. This active suction and pyrolysis unit 2
The combustion air in the combustion section is converted by the gas generated in
Flow is stopped. The high-temperature gas flowing out of the exhaust port 13 is used to heat the combustion air in the heat exchanger 8, then joins with the exhaust gas of the heating furnace described above, passes through the desuperheater 6 and the dust collector 7, and passes through the chimney. Released to the atmosphere from 91.

【0020】減温機6(ガス冷却機とも呼ばれる)は、
ガス通路に噴霧される噴霧水によって、ダイオキシンの
再合成温度領域を急冷却している。集塵機7はマルチサ
イクロンやバグフィルターなどである。排ガス中の大き
な灰分は、減温機6内で噴霧水に捕捉されて重力分離
し、細かいものは集塵機7で分離しているが、灰分のほ
とんどは溶融部4において溶融排出されるので、排ガス
中の飛灰はほとんど生じない。
The cooler 6 (also called a gas cooler)
The re-synthesis temperature range of dioxin is rapidly cooled by the spray water sprayed into the gas passage. The dust collector 7 is a multicyclone, a bag filter, or the like. The large ash in the exhaust gas is captured by the spray water in the desuperheater 6 and separated by gravity. Fine particles are separated in the dust collector 7. Almost no fly ash is generated.

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

【図1】実施形態の一例を示すブロック図FIG. 1 is a block diagram showing an example of an embodiment.

【符号の説明】[Explanation of symbols]

2 熱分解部 3 燃焼部 4 溶融部 11 落下口 13 排気口 24 加熱パイプ 33 空気供給口 41 加熱バーナ 42 堰 2 Thermal decomposition section 3 Combustion section 4 Melting section 11 Drop port 13 Exhaust port 24 Heating pipe 33 Air supply port 41 Heating burner 42 Weir

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) F23G 5/16 ZAB F23J 1/08 F23J 1/08 F27B 1/08 Z F27B 1/08 1/10 1/10 B09B 3/00 303K (72)発明者 増井 芽 石川県金沢市観音堂町ホ7番地 株式会社 アクトリームラタ内 (72)発明者 木下 秀英 石川県金沢市観音堂町ホ7番地 株式会社 アクトリームラタ内 (72)発明者 池田 健治 石川県金沢市観音堂町ホ7番地 株式会社 アクトリームラタ内 Fターム(参考) 3K061 AA07 AA16 AA23 AB02 AB03 AC01 AC13 AC17 AC19 CA01 CA07 DA01 DA13 DA18 DA19 DB06 DB11 DB16 DB20 FA03 FA10 FA12 FA21 FA25 3K078 BA03 BA22 BA26 CA03 CA09 CA12 CA21 CA24 CA25 4D004 AA01 AC04 CA24 CA29 CA32 CB09 CB36 CB42 4K045 AA01 BA10 CA02 GA02 GB08 GD01 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) F23G 5/16 ZAB F23J 1/08 F23J 1/08 F27B 1/08 Z F27B 1/08 1/10 1 / 10 B09B 3/00 303K (72) Inventor Mei Mei 7 in Kannon-do-cho, Kanazawa-shi, Ishikawa Prefecture Inside (72) Inventor Hidehide Kinoshita 7 in Kannon-do-cho, Kanazawa-shi, Ishikawa Prefecture (Actly Murata in ( 72) Inventor Kenji Ikeda 7 Kannondo-cho, Kanazawa-shi, Ishikawa F-term in Actley Murata Co., Ltd. 3K078 BA03 BA22 BA26 CA03 CA09 CA12 CA21 CA24 CA25 4D004 AA01 AC04 CA24 CA29 CA32 CB09 CB36 CB42 4K045 AA01 BA10 CA02 GA02 GB08 GD01

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 上部の熱分解部と下部の溶融部との間に
燃焼部を設け、熱分解部の残留固形分を重力落下により
熱分解ガスと共に燃焼部及び溶融部に移送し、熱分解ガ
スと固形物を分離しないで燃焼部で燃焼し、燃焼部を通
過した固形物を燃焼部の下方の溶融部で溶融することを
特徴とする、熱分解ガス化溶融炉。
1. A combustion section is provided between an upper thermal decomposition section and a lower melting section, and residual solids in the thermal decomposition section are transferred to the combustion section and the melting section together with the pyrolysis gas by gravity drop by thermal decomposition. A pyrolysis gasification and melting furnace, characterized in that gas and solid matter are burned in a combustion part without being separated, and solid matter that has passed through the combustion part is melted in a melting part below the combustion part.
【請求項2】 還元性雰囲気下で材料を加熱する熱分解
部(2)と、熱分解部で生じた可燃性ガスを燃焼する燃焼
部(3)と、残存した固形物を溶融する溶融部(4)とを一体
の炉体内に連続する空間として備え、熱分解部(2)は燃
焼部(3)の上方に位置し、燃焼部(3)は溶融部(4)の上方
に位置しており、熱分解部(2)は輻射加熱手段(24)と燃
焼部(3)の頂部に連通する材料の落下口(11)とを備え、
燃焼部(3)は燃焼空気の供給口(33)を備え、溶融部(4)は
その底部に溶融物の落下口と燃焼ガスを吸引する排気口
(13)とを備えている、熱分解ガス化溶融炉。
2. A pyrolysis section (2) for heating a material in a reducing atmosphere, a combustion section (3) for burning a combustible gas generated in the pyrolysis section, and a melting section for melting the remaining solid matter. (4) is provided as a continuous space in the integral furnace body, the pyrolysis section (2) is located above the combustion section (3), and the combustion section (3) is located above the melting section (4). The pyrolysis section (2) includes a radiant heating means (24) and a material drop port (11) communicating with the top of the combustion section (3),
The combustion part (3) is provided with a supply port (33) for combustion air, and the melting part (4) is provided at the bottom with a drop for molten material and an exhaust port for sucking combustion gas
(13) A pyrolysis gasification / melting furnace comprising:
【請求項3】 熱分解部(2)は材料を略水平方向に移送
する移送手段(22)を備えた略水平な炉内空間を形成して
おり、燃焼部(3)は重力落下により熱分解部(2)からの残
存固形物を溶融部(4)に導く上下方向に長い炉内空間を
形成しており、溶融部(4)は底面が傾斜した略水平方向
の炉内空間を形成している、請求項2記載の熱分解ガス
化溶融炉。
The pyrolysis section (2) forms a substantially horizontal furnace space provided with a transfer means (22) for transferring the material in a substantially horizontal direction, and the combustion section (3) is heated by gravity. A vertically long furnace space is formed to guide the remaining solid matter from the decomposition part (2) to the melting part (4), and the melting part (4) forms a substantially horizontal furnace space with a slanted bottom. 3. The pyrolysis gasification and melting furnace according to claim 2, wherein
【請求項4】 溶融部(4)が固形物の温度を高温に維持
する加熱バーナ(41)と溶融スラグの流下を制限する堰(4
2)を備えている、請求項3記載の熱分解ガス化溶融炉。
A melting part (4) has a heating burner (41) for maintaining the temperature of the solid material at a high temperature and a weir (4) for restricting the flow of molten slag.
4. The pyrolysis gasification and melting furnace according to claim 3, further comprising (2).
JP2000273609A 2000-09-08 2000-09-08 Pyrolytic gasification melting furnace for waste Pending JP2002081623A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000273609A JP2002081623A (en) 2000-09-08 2000-09-08 Pyrolytic gasification melting furnace for waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000273609A JP2002081623A (en) 2000-09-08 2000-09-08 Pyrolytic gasification melting furnace for waste

Publications (1)

Publication Number Publication Date
JP2002081623A true JP2002081623A (en) 2002-03-22

Family

ID=18759518

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000273609A Pending JP2002081623A (en) 2000-09-08 2000-09-08 Pyrolytic gasification melting furnace for waste

Country Status (1)

Country Link
JP (1) JP2002081623A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8307770B2 (en) 2006-03-10 2012-11-13 Pyropure Limited Waste treatment apparatus and method
GB2511756A (en) * 2013-03-11 2014-09-17 Envirofusion Ltd A Reactor for Processing Feed Material

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8307770B2 (en) 2006-03-10 2012-11-13 Pyropure Limited Waste treatment apparatus and method
US9851100B2 (en) 2006-03-10 2017-12-26 Pyropure Limited Waste treatment apparatus and method
GB2511756A (en) * 2013-03-11 2014-09-17 Envirofusion Ltd A Reactor for Processing Feed Material

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