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JPH10332125A - Waste treatment equipment - Google Patents

Waste treatment equipment

Info

Publication number
JPH10332125A
JPH10332125A JP14413797A JP14413797A JPH10332125A JP H10332125 A JPH10332125 A JP H10332125A JP 14413797 A JP14413797 A JP 14413797A JP 14413797 A JP14413797 A JP 14413797A JP H10332125 A JPH10332125 A JP H10332125A
Authority
JP
Japan
Prior art keywords
gas
waste
pressure
pyrolysis
combustion
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Withdrawn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
JP14413797A
Other languages
Japanese (ja)
Inventor
Yuya Yamahata
祐哉 山畑
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 JP14413797A priority Critical patent/JPH10332125A/en
Publication of JPH10332125A publication Critical patent/JPH10332125A/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Withdrawn legal-status Critical Current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
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

Landscapes

  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Chimneys And Flues (AREA)
  • Processing Of Solid Wastes (AREA)
  • Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

(57)【要約】 【課題】停電時に装置の停止後も、熱分解反応炉で残熱
により発生する乾留ガスを、停電スタック等の大型の付
設装置を設けることなく、装置の乾留ガスを大気圧以下
すなわち負圧に維持して、装置周辺への漏出等の公害の
発生を防止できる、廃棄物処理装置を提供する。 【解決手段】熱分解反応器で廃棄物を熱分解して得られ
る乾留ガスと、熱分解残留物の中から分離した燃焼性成
分とを燃焼溶融炉で燃焼処理する際に、商用電源で駆動
されるモータを動力源とする誘引送風機によって、該装
置の乾留ガス及び燃焼ガスの通路内を負圧に保持する廃
棄物処理装置において、停電時に前記誘引送風機の駆動
源を商用電源から、誘引送風機に着脱可能に併設した蒸
気タービンに切り換えて、前記乾留ガスを大気中に排出
するように構成する。
(57) [Problem] To reduce the carbonization gas generated by residual heat in a pyrolysis reactor even after the equipment is shut down during a power outage without using large-scale attached equipment such as a power outage stack. Provided is a waste disposal apparatus capable of preventing pollution such as leakage to the periphery of the apparatus while maintaining the pressure at a pressure equal to or lower than the atmospheric pressure, that is, a negative pressure. In a combustion furnace, a dry distillation gas obtained by pyrolyzing waste in a pyrolysis reactor and a combustible component separated from the pyrolysis residue are driven by a commercial power supply. In a waste treatment apparatus that keeps the inside of the passage of the dry distillation gas and the combustion gas at a negative pressure by an induced blower powered by a driven motor, the drive source of the induced blower is changed from a commercial power supply to an induced blower during a power failure. The gas turbine is configured to be switched to a steam turbine that is detachably attached to the gas turbine, and the carbonized gas is discharged into the atmosphere.

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、廃棄物を熱分解炉
で熱分解し、熱分解後の可燃成分を燃焼溶融炉で燃焼処
理する廃棄物処理装置において、熱分解炉で発生する乾
留ガスを、停電時でも装置内を負圧に維持して排出でき
る廃棄物処理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 waste treatment apparatus for thermally decomposing waste in a pyrolysis furnace and combusting combustible components after the pyrolysis in a combustion melting furnace. The present invention relates to a waste disposal apparatus capable of maintaining the inside of the apparatus at a negative pressure even during a power failure and discharging the waste.

【0002】[0002]

【従来の技術】一般廃棄物や廃プラスチックなどの可燃
物を含む都市ゴミ等を処理する産業廃棄物の処理装置の
一つに、廃棄物を熱分解反応器に供給し、低酸素雰囲気
中において加熱して乾留ガスと主として不揮発性成分と
からなる熱分解残留物に熱分解し、この熱分解残留物を
冷却した後に分離装置に供給して燃焼性成分と不燃焼性
成分とに分離して、この燃焼性成分と前記した乾留ガス
とを燃焼溶融炉で燃焼処理する廃棄物処理装置が知られ
ている。
2. Description of the Related Art One of industrial waste treatment apparatuses for treating municipal garbage and the like containing combustibles such as general waste and waste plastics is provided by supplying the waste to a pyrolysis reactor in a low oxygen atmosphere. It is thermally decomposed into a pyrolysis residue consisting of a dry distillation gas and mainly non-volatile components, and after cooling this pyrolysis residue, it is supplied to a separator to separate it into a combustible component and a non-combustible component. There is known a waste treatment apparatus for performing a combustion treatment of this combustible component and the above-mentioned dry distillation gas in a combustion melting furnace.

【0003】この廃棄物処理装置では、図4に示すよう
に、所定の大きさに破砕された廃棄物aは、ホッパー1
を経由して、熱分解反応器2に供給され、低酸素雰囲気
中で加熱されて熱分解される。この熱分解反応炉2は、
通常は横型回転式ドラムで構成され、図示しないシール
機構によりシールされて、低酸素雰囲気で、しかも、誘
引送風機3により内部は大気圧以下に保持される。ま
た、この熱分解反応炉2の加熱は、燃焼溶融炉4の後流
側に配置された高温空気加熱器5により加熱されてライ
ンL1を経由して供給される加熱空気bによって行わ
れ、熱分解反応炉2の内部は300℃〜600℃に、通
常は約450℃程度に加熱される。
[0003] In this waste treatment apparatus, as shown in FIG.
Is supplied to the thermal decomposition reactor 2 and is heated and pyrolyzed in a low oxygen atmosphere. This pyrolysis reactor 2
Usually, it is composed of a horizontal rotary drum, and is sealed by a sealing mechanism (not shown), and is kept in a low-oxygen atmosphere at an atmospheric pressure or lower by an induction blower 3. The heating of the pyrolysis reaction furnace 2 is performed by the heated air b which is heated by the high-temperature air heater 5 arranged on the downstream side of the combustion melting furnace 4 and supplied through the line L1. The inside of the decomposition reactor 2 is heated to 300 ° C. to 600 ° C., usually about 450 ° C.

【0004】この高温の低酸素雰囲気内に供給された廃
棄物aは熱分解して、乾留ガスG1と主として不揮発性
成分である熱分解残留物cとになり、排出装置6で熱分
解残留物cと分離された乾留ガスG1はラインL2を経
由して燃焼溶融炉4のバーナ7に供給され、燃焼処理さ
れる。一方の熱分解残留物cは、冷却装置8で約80℃
程度まで冷却された後に分離装置9に供給され、カーボ
ンを主体とする燃焼性成分dと、金属や陶器、砂利、コ
ンクリート片等のガレキよりなる不燃焼性成分eとに分
離され、不燃焼性成分eはコンテナ10に回収され、燃
焼性成分dは粉砕機11に送られて、例えば1mm以下の
微粉に粉砕された後、ラインL3を経由して、燃焼溶融
炉4のバーナ7に供給される。
The waste a supplied in the high-temperature low-oxygen atmosphere is thermally decomposed into a carbonization gas G1 and a pyrolysis residue c which is mainly a non-volatile component. The carbonization gas G1 separated from c is supplied to the burner 7 of the combustion melting furnace 4 via a line L2, and is subjected to a combustion treatment. On the other hand, the thermal decomposition residue c is cooled to about 80 ° C.
After being cooled to the extent, it is supplied to the separation device 9 and separated into a combustible component d mainly composed of carbon and an incombustible component e composed of rubble such as metal, pottery, gravel, concrete pieces, etc. The component e is collected in the container 10, and the combustible component d is sent to the crusher 11 and crushed into fine powder having a size of, for example, 1 mm or less, and then supplied to the burner 7 of the combustion melting furnace 4 via the line L3. You.

【0005】燃焼溶融炉4においては、微粉化された燃
焼性成分dは、乾留ガスG1と共に、押込送風機12か
らラインL4経由で供給される燃焼用空気fとにより、
約1,300℃程度の高温域で燃焼処理される。この燃
焼処理により発生する燃焼ガスG2は、ラインL5に設
けられた高温空気加熱器5および発電装置20に蒸気を
供給する廃熱ボイラ14により熱回収され、その後、集
塵装置15とガス洗浄装置16で除塵及び洗浄されクリ
ーンな比較的低温の排ガスG3となって、その一部は、
ラインL6の押込送風機19によってイナートガスとし
て冷却装置8に供給され、大部分は煙突17から大気へ
放出される。
[0005] In the combustion melting furnace 4, the pulverized combustible component d is produced by the combustion air f supplied from the push-in blower 12 via the line L 4 together with the carbonization gas G 1.
Combustion treatment is performed in a high temperature range of about 1,300 ° C. The combustion gas G2 generated by this combustion process is recovered by the waste heat boiler 14 that supplies steam to the high-temperature air heater 5 and the power generation device 20 provided in the line L5, and then the dust collection device 15 and the gas cleaning device. The dust is cleaned and removed at 16 to become a clean relatively low-temperature exhaust gas G3.
The cooling gas is supplied to the cooling device 8 as inert gas by the forced blower 19 in the line L6, and most of the gas is discharged from the chimney 17 to the atmosphere.

【0006】一方、この燃焼処理により発生する燃焼灰
は溶融スラグgとなって燃焼溶融炉4の炉壁を流下し、
下部の水槽13の水中に落下して冷却固化される。この
廃棄物処理装置においては、熱分解反応器2や燃焼溶融
炉4内を大気圧以下の負圧に保持して、乾留ガスや燃焼
ガスが漏出しないようにするために、商用電源を駆動源
とするモータ18により駆動される誘引送風機3を設け
ている。
On the other hand, the combustion ash generated by this combustion treatment becomes molten slag g and flows down the furnace wall of the combustion and melting furnace 4.
It falls into the water in the lower water tank 13 and is cooled and solidified. In this waste treatment apparatus, a commercial power supply is used as a driving source in order to keep the inside of the pyrolysis reactor 2 and the combustion melting furnace 4 at a negative pressure lower than the atmospheric pressure and to prevent the carbonization gas and the combustion gas from leaking. The induction blower 3 driven by the motor 18 is provided.

【0007】[0007]

【発明が解決しようとする課題】ところで、この廃棄物
処理装置において、商用電源の停電等が発生して、誘引
送風機3が停止した場合、廃棄物処理装置の運転が停止
した後でも、熱分解反応器2では、残熱のため乾留ガス
G1の発生が継続するため、そのまま放置すると、熱分
解反応器2や燃焼溶融炉4の内部に可燃性の乾留ガスG
1が充満して、内部の圧力が高まり負圧から正圧になる
と、乾留ガスG1が炉や配管の外部へ漏出する恐れがあ
る。
In this waste treatment apparatus, if the induction blower 3 is stopped due to a power failure of a commercial power supply or the like, the thermal decomposition is performed even after the operation of the waste treatment apparatus is stopped. In the reactor 2, since the generation of the carbonization gas G1 continues due to residual heat, if left as it is, the flammable carbonization gas G1 will remain inside the pyrolysis reactor 2 and the combustion melting furnace 4.
When 1 is filled and the internal pressure increases to change from negative pressure to positive pressure, the carbonization gas G1 may leak to the outside of the furnace or the piping.

【0008】そこで、前記したような従来の廃棄物処理
装置では、停電等の事態を想定して、通常運転時に使用
しない特別の停電スタックを設けている。すなわち、ラ
インL2 に分岐管を設け、この分岐管を停電スタックに
連結し、停電時にはこの乾留ガスG1を停電スタックに
供給して燃焼させ、大気へ放出するようにしている。こ
の停電スタックは通常は大型の煙突状の構造物であり、
かつ不時のため常時内部で点火用のバーナを作動させる
必要がある。そのため、装置の据付場所の面積が広くな
るばかりでなく、建設費の増大や建設工期の長期化や補
助燃料が必要になるなどの問題がある。
Therefore, in the above-mentioned conventional waste disposal apparatus, a special power failure stack not used during normal operation is provided in consideration of a power failure or the like. That is, a branch pipe is provided in the line L2, and this branch pipe is connected to the power failure stack. In the event of a power failure, the dry distillation gas G1 is supplied to the power failure stack, burned, and released to the atmosphere. This power outage stack is usually a large chimney-like structure,
At the same time, it is necessary to always operate the burner for ignition internally. Therefore, not only is the area of the installation site of the apparatus large, but also the construction cost is increased, the construction period is lengthened, and auxiliary fuel is required.

【0009】本発明の目的は、停電時に装置の停止後
も、熱分解反応炉で残熱により発生する乾留ガスを、停
電スタック等の大型の付設装置を設けることなく、装置
の乾留ガスを大気圧以下すなわち負圧に維持して、装置
周辺への漏出等の公害の発生を防止できる、廃棄物処理
装置を提供することにある。
[0009] An object of the present invention is to reduce the carbonization gas generated by residual heat in a pyrolysis reactor even after the apparatus is shut down during a power outage without using a large-sized additional device such as a power outage stack. It is an object of the present invention to provide a waste treatment apparatus capable of preventing pollution such as leakage to the periphery of the apparatus while maintaining the pressure at a pressure equal to or lower than the atmospheric pressure, that is, a negative pressure.

【0010】[0010]

【課題を解決するための手段】本発明の廃棄物処理装置
は、廃棄物を、熱分解反応器で乾留ガスと熱分解残留物
とに熱分解し、該熱分解残留物を分離装置で燃焼性成分
と不燃焼性成分とに分離し、分離した前記燃焼性成分と
前記乾留ガスとを燃焼溶融炉に供給して燃焼処理すると
共に、商用電源を動力源とするモータによって駆動され
る誘引送風機によって、前記熱分解反応器と前記燃焼溶
融炉の内部圧力を大気圧以下に保持する廃棄物処理装置
において、前記誘引送風機に蒸気タービンを着脱可能に
併設し、停電時に前記誘引送風機の駆動源を前記モータ
から前記蒸気タービンに切り換えて、前記誘引送風機を
駆動して、前記乾留ガスを大気中へ排出するように構成
される。
According to the present invention, there is provided a waste treatment apparatus wherein a waste is pyrolyzed into a pyrolysis gas and a pyrolysis residue in a pyrolysis reactor, and the pyrolysis residue is burned in a separation device. An air blower driven by a motor powered by a commercial power supply while supplying the separated combustible component and the carbonized gas to a combustion melting furnace for combustion treatment by separating into a flammable component and a non-combustible component Thus, in a waste treatment apparatus that maintains the internal pressure of the pyrolysis reactor and the combustion melting furnace at or below atmospheric pressure, a steam turbine is detachably provided with the induction blower, and a drive source of the induction blower is provided during a power outage. The motor is switched to the steam turbine, and the induction blower is driven to discharge the carbonized gas into the atmosphere.

【0011】そして、好ましくは、前記燃焼溶融炉の内
部圧力を検出する圧力検出装置を設け、前記圧力検出装
置で検出した圧力値により、前記蒸気タービンへ供給す
る蒸気量を制御するように構成される。更に、好ましく
は、前記蒸気タービンに供給する蒸気を前記燃焼溶融炉
の後流側に配設した廃熱ボイラから得るのがよい。
Preferably, a pressure detecting device for detecting an internal pressure of the combustion melting furnace is provided, and the amount of steam supplied to the steam turbine is controlled by a pressure value detected by the pressure detecting device. You. More preferably, the steam to be supplied to the steam turbine is obtained from a waste heat boiler disposed downstream of the combustion melting furnace.

【0012】そして、前記乾留ガスを、大気中へ排出す
る前に白煙防止加熱炉で燃焼処理することで環境への影
響をより少なくできる。
[0012] By burning the carbonized gas in a white smoke prevention heating furnace before discharging it to the atmosphere, the effect on the environment can be reduced.

【0013】[0013]

【発明の実施の形態】図1は本発明の実施の形態の廃棄
物処理装置の系統図であり、図2は図1のA部の詳細図
である。これらの図において、図4と同一の符号を付し
たものは図4と同一の装置及び物質を示しており、又、
誘引送風機3の駆動に関する以下に説明する部分以外
は、先に説明した図4の廃棄物処理装置と同じであるの
で説明を省略する。
FIG. 1 is a system diagram of a waste disposal apparatus according to an embodiment of the present invention, and FIG. 2 is a detailed view of a portion A in FIG. In these figures, the components denoted by the same reference numerals as those in FIG. 4 indicate the same devices and substances as those in FIG.
Except for the portion described below relating to the drive of the induction blower 3, it is the same as the previously described waste treatment apparatus of FIG.

【0014】この図1と図2において、蒸気タービン2
1が着脱装置22により誘引送風機3と連結可能に設け
られている。この着脱装置22は、廃棄物処理装置の通
常運転時において停電が生じて、誘引送風機3のモータ
18が停止すると図示しない検出装置の信号により、そ
れを検知して、蒸気タービン21と誘引送風機3とを連
結し、停電が解除されモータ18が駆動可能となると蒸
気タービン21と誘引送風機3の連結を解除するように
構成する。
1 and 2, a steam turbine 2
1 is provided so as to be able to be connected to the induction blower 3 by the attachment / detachment device 22. When a power outage occurs during the normal operation of the waste treatment device and the motor 18 of the induction blower 3 stops, the attachment / detachment device 22 detects this by a signal from a detection device (not shown), and detects the steam turbine 21 and the induction blower 3. And when the power failure is released and the motor 18 can be driven, the connection between the steam turbine 21 and the induction blower 3 is released.

【0015】この蒸気タービン21には制御弁23を有
するラインL7が設けられ廃熱ボイラ14で発生した蒸
気sの一部を受給できるように構成され、更に、燃焼溶
融炉4に配置された炉内圧力検出装置である圧力計24
からの信号V1が制御装置25に入力され、この制御装
置25で作成された制御信号V2によって制御弁23が
開閉して、蒸気タービン21に供給される蒸気sの流量
を制御するように構成される。
The steam turbine 21 is provided with a line L 7 having a control valve 23 so as to be able to receive a part of the steam s generated in the waste heat boiler 14. Pressure gauge 24 as internal pressure detector
Is input to the control device 25, and the control valve 23 is opened and closed by the control signal V2 generated by the control device 25 to control the flow rate of the steam s supplied to the steam turbine 21. You.

【0016】更に、熱分解反応器2で発生する乾留ガス
G1がラインL2を経由して燃焼溶融炉4内に流入し炉
内圧力を上昇させると、この圧力上昇を圧力計24が検
知し、その信号V1が制御装置25に入力され、制御信
号V2により制御弁23の開度を調整して蒸気タービン
21に供給する蒸気量を制御して蒸気タービンの回転、
及び誘引送風機3の回転を制御するように構成する。
Further, when the dry distillation gas G1 generated in the pyrolysis reactor 2 flows into the combustion and melting furnace 4 via the line L2 and raises the pressure in the furnace, the pressure rise is detected by the pressure gauge 24. The signal V1 is input to the control device 25, the opening of the control valve 23 is adjusted by the control signal V2 to control the amount of steam supplied to the steam turbine 21, and the rotation of the steam turbine is controlled.
And it controls so that rotation of the induction blower 3 may be controlled.

【0017】又、乾留ガスG1を燃焼処理してから大気
中に開放する場合は、図3に示すように誘引送風機3に
より誘引された乾留ガスG1を三方弁26を経て分岐管
27に設けた白煙防止加熱炉28に導入して燃焼処理
し、その燃焼ガスG4を煙突17から排出するように構
成する。以上の構成の廃棄物処理装置によれば、停電時
に、誘引送風機3の駆動源をモータ18から蒸気タービ
ン21に切り換えて、燃焼溶融炉の炉内圧力を検出し
て、廃熱ボイラ14の残熱で発生する蒸気を蒸気タービ
ン21に供給して、この蒸気タービン21で誘引送風機
3を駆動し、運転を停止した熱分解反応器2から残熱に
より発生を継続している乾留ガスG1を、大気中へ放出
することができる。
When the carbonized gas G1 is burned and then released into the atmosphere, the carbonized gas G1 introduced by the induction blower 3 is provided to the branch pipe 27 via the three-way valve 26 as shown in FIG. The combustion gas G4 is introduced into the white smoke prevention heating furnace 28 and burned, and the combustion gas G4 is discharged from the chimney 17. According to the waste treatment apparatus having the above-described configuration, at the time of a power failure, the drive source of the induction blower 3 is switched from the motor 18 to the steam turbine 21 to detect the pressure in the furnace of the combustion melting furnace. The steam generated by heat is supplied to the steam turbine 21, and the induction blower 3 is driven by the steam turbine 21, and the pyrolysis gas G <b> 1 continuously generated by the residual heat from the pyrolysis reactor 2 whose operation has been stopped is converted into Can be released to the atmosphere.

【0018】また、燃焼溶融炉4の炉内圧力に基づい
て、誘引送風機3を駆動して誘引力を発生させるととも
に、その誘引力の大きさを調整することができので、熱
分解反応器2や燃焼溶融炉4やラインL2,L5の乾留
ガスG1を煙突17を経由して大気中へ放出して、熱分
解反応器2や燃焼溶融炉4やラインL2,L5を負圧に
保持でき、これらの部分における可燃性の乾留ガスG1
の漏洩を防止することができる。
Further, based on the pressure in the furnace 4 of the combustion and melting furnace, the attracting force can be generated by driving the attracting blower 3 and the magnitude of the attracting force can be adjusted. And the carbonization gas G1 from the combustion and melting furnace 4 and the lines L2 and L5 can be released into the atmosphere via the chimney 17 to maintain the pyrolysis reactor 2, the combustion and melting furnace 4 and the lines L2 and L5 at a negative pressure, Combustible carbonization gas G1 in these parts
Leakage can be prevented.

【0019】この蒸気タービン21へ供給する蒸気はこ
の廃熱ボイラ14で発生する蒸気に限られるものではな
く、他の蒸気源から導くようにしてもよく、又、この蒸
気タービン21への蒸気供給の制御は燃焼溶融炉4の炉
内圧力により制御されるばかりでなく、例えば停電の有
無を検知したり、熱分解反応器2の乾留ガスG1の発生
量を検知して、こ乾留ガスG1の発生量に基づいて蒸気
量を制御してもよい。
The steam supplied to the steam turbine 21 is not limited to the steam generated by the waste heat boiler 14, but may be derived from another steam source. Is controlled not only by the pressure in the furnace of the combustion and melting furnace 4 but also by detecting, for example, the presence or absence of a power outage, or by detecting the amount of the carbonized gas G1 generated in the pyrolysis reactor 2 to generate the carbonized gas G1. The amount of steam may be controlled based on the amount of generation.

【0020】[0020]

【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よれば、停電時に誘引送風機を
蒸気タービンにより駆動するように構成したため、特別
の停電スタックを設ける必要がない。従って、廃棄物処
理装置の全体構成を小型化することができ、据付場所の
必要面積を少なくすることができるとともに、建設費の
低減や建設工期の短縮を図ることができるという効果が
ある。
As is apparent from the above description, according to the waste treatment apparatus of the present invention, the induction blower is driven by the steam turbine at the time of power failure, so that there is no need to provide a special power failure stack. Therefore, the overall configuration of the waste treatment apparatus can be reduced in size, the required area of the installation place can be reduced, and the construction cost and the construction period can be reduced.

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

【図1】本発明の実施の形態の廃棄物処理装置の系統図
である。
FIG. 1 is a system diagram of a waste disposal apparatus according to an embodiment of the present invention.

【図2】図1のA部詳細図である。FIG. 2 is a detailed view of a portion A in FIG.

【図3】乾留ガスを白煙防止加熱炉で燃焼処理して排出
する場合の要部系統図である。
FIG. 3 is a main part system diagram in a case where a carbonization gas is subjected to a combustion treatment in a white smoke prevention heating furnace and discharged.

【図4】先行技術の廃棄物処理装置の系統図である。FIG. 4 is a system diagram of a prior art waste disposal apparatus.

【符号の説明】[Explanation of symbols]

1 ホッパー 2 熱分解反応器 3 誘引送風機 4 燃焼溶融炉 5 高温空気加熱器 6 排出装置 7 バーナ 8 冷却装置 9 分離装置 10 コンテナ 11 粉砕機 12,19 押込
送風機 13 水槽 14 廃熱ボイラ 15 集塵装置 16 ガス洗浄装
置 17 煙突 18 モータ 20 発電装置 21 蒸気タービ
ン 22 着脱装置 23 制御弁 24 圧力計 25 制御装置 26 三方弁 27 分岐管 28 白煙防止加熱炉
DESCRIPTION OF SYMBOLS 1 Hopper 2 Pyrolysis reactor 3 Induction blower 4 Combustion melting furnace 5 High temperature air heater 6 Discharge device 7 Burner 8 Cooling device 9 Separator 10 Container 11 Crusher 12, 19 Push-in blower 13 Water tank 14 Waste heat boiler 15 Dust collector Reference Signs List 16 gas cleaning device 17 chimney 18 motor 20 power generation device 21 steam turbine 22 attachment / detachment device 23 control valve 24 pressure gauge 25 control device 26 three-way valve 27 branch pipe 28 white smoke prevention heating furnace

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI // C08J 11/12 ZAB B09B 3/00 303G F23J 15/00 F ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification symbol FI // C08J 11/12 ZAB B09B 3/00 303G F23J 15/00 F

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 廃棄物を、熱分解反応器で乾留ガスと熱
分解残留物とに熱分解し、該熱分解残留物を分離装置で
燃焼性成分と不燃焼性成分とに分離し、分離した前記燃
焼性成分と前記乾留ガスとを燃焼溶融炉に供給して燃焼
処理すると共に、商用電源を動力源とするモータによっ
て駆動される誘引送風機によって、前記熱分解反応器と
前記燃焼溶融炉の内部圧力を大気圧以下に保持する廃棄
物処理装置において、前記誘引送風機に蒸気タービンを
着脱可能に併設し、停電時に前記誘引送風機の駆動源を
前記モータから前記蒸気タービンに切り換えて、前記誘
引送風機を駆動して、前記乾留ガスを大気中へ排出する
ように構成した廃棄物処理装置。
1. Pyrolysis of waste into pyrolysis gas and pyrolysis residue in a pyrolysis reactor, and separating the pyrolysis residue into a combustible component and a non-combustible component by a separation device. The combustible component and the carbonization gas are supplied to a combustion melting furnace to perform a combustion process, and an induction blower driven by a motor using a commercial power source as a power source causes the pyrolysis reactor and the combustion melting furnace to have the same configuration. In the waste treatment apparatus for maintaining the internal pressure at or below the atmospheric pressure, a steam turbine is detachably attached to the induction blower, and a drive source of the induction blower is switched from the motor to the steam turbine during a power outage, and the induction blower is used. And a waste disposal apparatus configured to drive the gas to discharge the carbonized gas into the atmosphere.
【請求項2】 前記燃焼溶融炉の内部圧力を検出する圧
力検出装置を設け、前記圧力検出装置で検出した圧力値
により、前記蒸気タービンへ供給する蒸気量を制御する
請求項1記載の廃棄物処理装置。
2. The waste according to claim 1, further comprising a pressure detection device for detecting an internal pressure of the combustion melting furnace, and controlling an amount of steam supplied to the steam turbine based on a pressure value detected by the pressure detection device. Processing equipment.
【請求項3】 前記蒸気タービンに供給する蒸気を前記
燃焼溶融炉の後流側に配設した廃熱ボイラから得る請求
項1又は2に記載の廃棄物処理装置。
3. The waste treatment apparatus according to claim 1, wherein the steam supplied to the steam turbine is obtained from a waste heat boiler disposed downstream of the combustion melting furnace.
【請求項4】 前記乾留ガスを、大気中へ排出する前に
白煙防止加熱炉で燃焼処理する請求項1〜3のいずれか
に記載の廃棄物処理装置。
4. The waste treatment apparatus according to claim 1, wherein the dry distillation gas is burned in a white smoke prevention heating furnace before being discharged into the atmosphere.
JP14413797A 1997-06-02 1997-06-02 Waste treatment equipment Withdrawn JPH10332125A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14413797A JPH10332125A (en) 1997-06-02 1997-06-02 Waste treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14413797A JPH10332125A (en) 1997-06-02 1997-06-02 Waste treatment equipment

Publications (1)

Publication Number Publication Date
JPH10332125A true JPH10332125A (en) 1998-12-15

Family

ID=15355089

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14413797A Withdrawn JPH10332125A (en) 1997-06-02 1997-06-02 Waste treatment equipment

Country Status (1)

Country Link
JP (1) JPH10332125A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPWO2007138965A1 (en) * 2006-05-25 2009-10-08 株式会社ブレスト Oiling equipment
CN102606236A (en) * 2012-03-22 2012-07-25 深圳市炬能生物质气化科技有限公司 Garbage disposal waste heat power generation system with internal steam pipe
CN107052023A (en) * 2017-03-31 2017-08-18 金华职业技术学院 Domestic waste boiling destructive distillation integrates method for separating and processing

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPWO2007138965A1 (en) * 2006-05-25 2009-10-08 株式会社ブレスト Oiling equipment
CN102606236A (en) * 2012-03-22 2012-07-25 深圳市炬能生物质气化科技有限公司 Garbage disposal waste heat power generation system with internal steam pipe
CN107052023A (en) * 2017-03-31 2017-08-18 金华职业技术学院 Domestic waste boiling destructive distillation integrates method for separating and processing
CN107052023B (en) * 2017-03-31 2019-06-18 金华职业技术学院 Comprehensive separation and treatment method of municipal solid waste cooking and dry distillation

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