JP3288164B2 - Waste plastic pyrolysis equipment - Google Patents

Waste plastic pyrolysis equipment

Info

Publication number
JP3288164B2
JP3288164B2 JP33690593A JP33690593A JP3288164B2 JP 3288164 B2 JP3288164 B2 JP 3288164B2 JP 33690593 A JP33690593 A JP 33690593A JP 33690593 A JP33690593 A JP 33690593A JP 3288164 B2 JP3288164 B2 JP 3288164B2
Authority
JP
Japan
Prior art keywords
tank
inner tank
waste plastic
outer tank
heat
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.)
Expired - Fee Related
Application number
JP33690593A
Other languages
Japanese (ja)
Other versions
JPH07197032A (en
Inventor
一雄 鈴木
仁弘 忠内
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.)
Toshiba Corp
Original Assignee
Toshiba 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 Toshiba Corp filed Critical Toshiba Corp
Priority to JP33690593A priority Critical patent/JP3288164B2/en
Priority to US08/262,185 priority patent/US5608136A/en
Priority to DE4446964A priority patent/DE4446964C2/en
Publication of JPH07197032A publication Critical patent/JPH07197032A/en
Priority to US09/033,921 priority patent/US6172275B1/en
Application granted granted Critical
Publication of JP3288164B2 publication Critical patent/JP3288164B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • C10G1/10Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal from rubber or rubber waste
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • C10B53/07Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of solid raw materials consisting of synthetic polymeric materials, e.g. tyres
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • C10G1/002Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal in combination with oil conversion- or refining processes
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • C10G1/006Combinations of processes provided in groups C10G1/02 - C10G1/08
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • C10G1/02Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal by distillation
    • 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
    • Y02P20/143Feedstock the feedstock being recycled material, e.g. plastics

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、廃プラスチックの熱分
解装置、更に詳しくは、廃プラスチックを熱分解して燃
料油を回収するための熱分解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 pyrolysis apparatus for waste plastics, and more particularly to a pyrolysis apparatus for pyrolyzing waste plastics to recover fuel oil.

【0002】[0002]

【従来の技術】廃プラスチックを処理する方法として、
古くから、加熱処理して容積を減少させる技術や焼却す
る技術が知られている。廃プラスチック、特に塩化ビニ
ル樹脂等を熱分解すると、装置内に残渣が生成する。
又、資源の有効利用の観点から、最近は、ゴミとして廃
棄されるプラスチックそのものの容積を減少させるだけ
ではなく、燃料油として再資源化することが注目されつ
つあるが、この場合においても、分解槽内に粘着性又は
微粒子状の残渣が生成する。従って、加熱処理後には残
渣の掻き出し作業が必要となる。特に、バッチ方式処理
のような場合には、残渣の書き出し作業中は装置の作動
を停止しなければならず、廃プラスチックの分解装置へ
の受け入れ時における作動停止も考慮すると、1日当た
りの処理量は大幅に制限される。
2. Description of the Related Art As a method of treating waste plastic,
For a long time, a technology for reducing the volume by heat treatment and a technology for incineration have been known. When waste plastics, especially vinyl chloride resin, are thermally decomposed, residues are generated in the apparatus.
In addition, from the viewpoint of effective use of resources, recently, not only reducing the volume of plastic itself discarded as garbage, but also recycling it as fuel oil has been attracting attention. Sticky or particulate residue is formed in the tank. Therefore, it is necessary to scrape out the residue after the heat treatment. In particular, in the case of batch processing, the operation of the equipment must be stopped during the work of writing out the residue. Is severely restricted.

【0003】[0003]

【発明が解決しようとする課題】ところが、近年、最終
処分場などの処理施設の確保が困難になり、廃棄物処理
も大きな社会問題と化している。このような状況におい
て、分解装置の処理能力を上げ、廃プラスチックを効率
よく再資源化できるようにすることが急務とされるよう
になった。又、分解槽内の掻き出し作業は容易ではな
く、粉塵等によって作業者の健康を害する可能性も大き
い。
However, in recent years, it has become difficult to secure treatment facilities such as a final disposal site, and waste disposal has become a major social problem. In such a situation, there is an urgent need to increase the processing capacity of the decomposer so that waste plastic can be efficiently recycled. In addition, the scraping operation in the disassembling tank is not easy, and there is a great possibility that the worker's health is impaired by dust or the like.

【0004】本発明は、このような従来の問題点に鑑み
てなされたもので、廃プラスチックの分解再資源化と残
渣の処理を効率よく行うことができ、残渣の処理が容易
な廃プラスチックの熱分解装置を提供することを目的と
するものである。
[0004] The present invention has been made in view of such conventional problems, and can efficiently decompose and recycle waste plastic and treat the residue, and can easily treat the residue. It is an object of the present invention to provide a pyrolysis apparatus.

【0005】[0005]

【課題を解決するための手段】上記目的を達成するため
に、本発明者らは鋭意研究を重ねた結果、2重槽式加熱
分解装置を用いることによって残渣処理が効率よく容易
に行え、2つの槽に相対応する伝熱部を設けることによ
って加熱分解の能率が向上することを見いだし、本発明
の熱分解装置を発明するに至った。
Means for Solving the Problems In order to achieve the above object, the present inventors have conducted intensive studies. As a result, the use of a double-tank type pyrolysis apparatus enables efficient and easy treatment of residues. It has been found that the efficiency of thermal decomposition is improved by providing the corresponding heat transfer sections in two tanks, and the inventors have invented the thermal decomposition apparatus of the present invention.

【0006】本発明の熱分解装置は、廃プラスチックを
熱分解して燃料油を回収する熱分解装置であって、加熱
手段によって加熱される外槽と、外槽内に出し入れ可能
な廃プラスチックを収容するための内槽とを備え、該外
槽が、加熱時に内槽表面と密接して外槽から内槽への熱
伝導性を高めるための熱伝導部を有するものである。
The pyrolysis apparatus of the present invention is a pyrolysis apparatus for recovering fuel oil by pyrolyzing waste plastic, and comprises an outer tank heated by a heating means, and a waste plastic that can be taken in and out of the outer tank. An inner tank for housing the outer tank, wherein the outer tank has a heat conducting part for increasing heat conductivity from the outer tank to the inner tank in close contact with the inner tank surface during heating.

【0007】又、前記熱伝導部は内径Dの円筒形の仕切
り板で形成され、前記内槽は直径dの円筒容器で形成さ
れるに際し、d/Dは、0.7<d/D≦0.98に設
定される。
Further, when the heat conducting portion is formed by a cylindrical partition plate having an inner diameter D, and the inner tank is formed by a cylindrical container having a diameter d, d / D is 0.7 <d / D ≦ Set to 0.98.

【0008】[0008]

【作用】廃プラスチックを収容する内槽は外槽内に入れ
られ、内槽表面と外槽の熱伝導部とが密接する。加熱手
段によって外槽が加熱され、熱伝導部を通じて外槽から
内槽へ高い熱伝導性で熱が伝達され、内槽が加熱されて
廃プラスチックが熱分解される。分解終了後、内槽は外
槽から取り出され、内槽から残渣が除去される。
The inner tank containing the waste plastic is placed in the outer tank, and the surface of the inner tank is in close contact with the heat conducting portion of the outer tank. The outer tank is heated by the heating means, heat is transferred with high thermal conductivity from the outer tank to the inner tank through the heat conducting portion, and the inner tank is heated to thermally decompose waste plastic. After the decomposition, the inner tank is taken out of the outer tank, and the residue is removed from the inner tank.

【0009】[0009]

【実施例】以下、本発明について詳細に説明する。DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail.

【0010】熱分解装置はバッチ処理型であり、廃プラ
スチックを収容する分解槽と、分解槽内の廃プラスチッ
クを加熱分解するために分解槽を加熱する加熱手段を備
え、更に、廃プラスチックの熱分解によって生じた燃料
油分のガスを冷却等の処理によって液体燃料油として回
収する回収手段を備えている。
The thermal decomposition apparatus is of a batch processing type and includes a decomposition tank for storing waste plastic, and a heating means for heating the decomposition tank for thermally decomposing the waste plastic in the decomposition tank. A recovery unit is provided for recovering the fuel oil gas generated by the decomposition as liquid fuel oil by a process such as cooling.

【0011】本発明に係る分解装置は、まず、分解槽を
2重構造としていることに特徴がある。すなわち、分解
槽は互いに分離可能な外槽と内槽とからなり、外槽は加
熱手段によって直接加熱され、内槽は廃プラスチックを
収容して外槽内に据えられる。廃プラスチックの熱分解
後、内槽は分解プラスチック残渣と共に外槽の外へ引き
出され、残渣の掻き出しが行われる。その間、別の内槽
に収容された新たな廃プラスチックが外槽内に導入され
て加熱分解される。更に、本発明では、外槽から内槽へ
の熱伝導効率を向上させるために、外槽には、加熱時に
内槽の表面と密接するような熱伝導部が設けられてお
り、互いの表面が接触することによって熱が直接的に伝
わり、熱伝導が容易になる。熱伝導部は、内槽を下方か
ら加熱し熱分解が適切に行われるように工夫がなされ
る。
The decomposition apparatus according to the present invention is characterized in that the decomposition tank has a double structure. That is, the decomposition tank is composed of an outer tank and an inner tank that can be separated from each other, the outer tank is directly heated by the heating means, and the inner tank stores waste plastic and is set in the outer tank. After the thermal decomposition of the waste plastic, the inner tank is drawn out of the outer tank together with the decomposed plastic residue, and the residue is scraped out. During that time, new waste plastic stored in another inner tank is introduced into the outer tank and decomposed by heating. Furthermore, in the present invention, in order to improve the efficiency of heat conduction from the outer tank to the inner tank, the outer tank is provided with a heat conducting portion that is in close contact with the surface of the inner tank when heated, and the surfaces of the outer tank are provided with each other. The heat is directly transmitted by the contact of the metal, and heat conduction is facilitated. The heat conducting part is devised so that the inner tank is heated from below to perform the thermal decomposition appropriately.

【0012】以下、図面を参照しながら、実施例を用い
て本発明をさらに詳細に説明する。図1及び図2に示さ
れるように、熱分解装置は、内槽1及び外槽3を備え
る。この実施例における内槽1は円筒形状の側壁1aと
円形底部1bとを備える。内槽1には、運搬用のフック
又は取っ手(図示せず)が設けられている。内槽1はジ
ブクレーン5を用いて搬送され、外槽3は、内槽1を外
槽3内に導入するために開閉されるハッチ7を頂部に有
する。図2に示されるように、外槽3の仕切り板3a中
央には円筒形状の凹部3bが形成され、内槽1がこの中
に嵌入される。外槽3の下部に仕切り板3aに仕切られ
燃焼室9が一体的に形成され、燃焼室9に据え付けられ
たバーナー11での燃焼によって仕切り板3aを含む外
槽3が加熱される。加熱時に、仕切り板3aの熱は、内
槽1の凹部3bと接する部分を通じて内槽1に伝達され
る。
Hereinafter, the present invention will be described in more detail using embodiments with reference to the drawings. As shown in FIGS. 1 and 2, the thermal decomposition apparatus includes an inner tank 1 and an outer tank 3. The inner tank 1 in this embodiment has a cylindrical side wall 1a and a circular bottom 1b. The inner tank 1 is provided with a transport hook or handle (not shown). The inner tank 1 is transported using a jib crane 5, and the outer tank 3 has a hatch 7 at the top which is opened and closed to introduce the inner tank 1 into the outer tank 3. As shown in FIG. 2, a cylindrical concave portion 3b is formed at the center of the partition plate 3a of the outer tank 3, and the inner tank 1 is fitted therein. A combustion chamber 9 is formed integrally with a partition plate 3a at a lower portion of the outer tub 3 and the outer tub 3 including the partition plate 3a is heated by combustion by a burner 11 installed in the combustion chamber 9. At the time of heating, the heat of the partition plate 3a is transmitted to the inner tank 1 through a portion of the inner tank 1 that contacts the recess 3b.

【0013】更に、内槽1及び外槽3の内部の温度を検
出するための温度検出器13a、13bがハッチ7及び
外槽壁部を介して外槽3内に導入されている。温度検出
器13によって検知された温度を制御変数としてバーナ
ー11の加熱量を制御するための温度制御演算器15が
温度検出器13及びバーナー11に接続されている。
Further, temperature detectors 13a and 13b for detecting the temperatures inside the inner tank 1 and the outer tank 3 are introduced into the outer tank 3 through the hatch 7 and the outer tank wall. A temperature control calculator 15 for controlling the heating amount of the burner 11 using the temperature detected by the temperature detector 13 as a control variable is connected to the temperature detector 13 and the burner 11.

【0014】又、廃プラスチックの分解によって生じる
ガス状燃料油分を外槽3外部へ配送するための配管15
が外槽3に接続され、図1に示すように、配管15の流
体流量を検出するための流量検出器17が取り付けられ
ている。更に、配管15には流量を調節する調節弁19
が設けられており、流量検出器17によって検出された
流量を制御変数として流量制御演算器21によって制御
されるように構成されている。又、外槽3内の気体圧力
を検出するための圧力検出器23が取り付けられてい
る。
A pipe 15 for delivering gaseous fuel oil generated by decomposition of waste plastic to the outside of the outer tank 3.
Is connected to the outer tank 3, and a flow rate detector 17 for detecting the fluid flow rate of the pipe 15 is attached as shown in FIG. Further, a control valve 19 for adjusting the flow rate is provided in the pipe 15.
Is provided, and is configured to be controlled by the flow rate control calculator 21 using the flow rate detected by the flow rate detector 17 as a control variable. Further, a pressure detector 23 for detecting a gas pressure in the outer tank 3 is attached.

【0015】更に、配管15は一次凝縮器25及び二次
凝縮器27を通じて排ガス処理装置29に接続される。
一次凝縮器25及び二次凝縮器27は、重質分貯蔵タン
ク31及び軽質分貯蔵タンク33にそれぞれ接続され
る。一方、燃焼室9は、燃焼排ガスを処理するための排
ガス処理装置35に接続される。
Further, the pipe 15 is connected to an exhaust gas treatment device 29 through a primary condenser 25 and a secondary condenser 27.
The primary condenser 25 and the secondary condenser 27 are connected to a heavy component storage tank 31 and a light component storage tank 33, respectively. On the other hand, the combustion chamber 9 is connected to an exhaust gas treatment device 35 for treating combustion exhaust gas.

【0016】上記構成において、廃プラスチックの処理
は以下のようになされる。
In the above configuration, the treatment of the waste plastic is performed as follows.

【0017】まず、ハロゲンを含むプラスチックに対処
するために脱ハロゲンを促進する薬剤として水酸化ナト
リウム等のアルカリを添加した廃プラスチックPの粉粒
体・破砕流状物を内槽1内に収容して、内槽1をジブク
レーン5で外槽3上に持ち上げ、ハッチ7を開けて、外
槽3の凹部3bに内槽1を設置する。次に、バーナー1
1を点火して仕切り板3aを加熱すると、内槽1の仕切
り板3aと接している部分を通じて熱が伝達され、廃プ
ラスチックPが加熱される。加熱を続けると、廃プラス
チックの熱分解によって燃料油成分を含むガスが生成
し、外槽3内部に充満・乾留して油分への改質が促進さ
れる。廃プラスチックの温度が検出器13によって検出
され、これに応じてバーナー11の燃焼が制御され、内
槽1内部の温度は、好ましくは400〜500℃に調節
される。ガス状燃料油分を含む生成ガスは配管15を流
れ、この間、流量が調節弁19によって適宜調節され
る。外槽3内の圧力が急激に変動するような場合は調節
弁19が開閉される。生成ガスは一次凝縮器25に達し
て冷却され、重質分の多い液化成分101が凝縮分離し
て重質分貯蔵タンク31に貯蔵される。ガスは、更に二
次凝縮器27で冷却され、灯油などの軽質分の多い液化
成分103が凝縮分離して軽質分貯蔵タンク33に貯蔵
される。凝縮されないガス成分は排ガス処理装置35に
送られ、大気中へ放出可能となるように処理される。
First, in order to deal with a plastic containing halogen, a granular material or a crushed flow of waste plastic P to which an alkali such as sodium hydroxide is added as an agent for promoting dehalogenation is accommodated in the inner tank 1. Then, the inner tank 1 is lifted above the outer tank 3 by the jib crane 5, the hatch 7 is opened, and the inner tank 1 is set in the concave portion 3 b of the outer tank 3. Next, burner 1
When the partition plate 3a is heated by igniting 1, the heat is transferred through the portion of the inner tank 1 that is in contact with the partition plate 3a, and the waste plastic P is heated. When the heating is continued, a gas containing a fuel oil component is generated by thermal decomposition of the waste plastic, and the inside of the outer tank 3 is filled and dry-distilled to promote the reforming into oil. The temperature of the waste plastic is detected by the detector 13, the combustion of the burner 11 is controlled accordingly, and the temperature inside the inner tank 1 is preferably adjusted to 400 to 500 ° C. The product gas containing the gaseous fuel oil flows through the pipe 15, during which the flow rate is appropriately adjusted by the control valve 19. When the pressure in the outer tub 3 fluctuates rapidly, the control valve 19 is opened and closed. The produced gas reaches the primary condenser 25 where it is cooled, and the liquefied component 101 containing a large amount of heavy matter is condensed and separated and stored in the heavy matter storage tank 31. The gas is further cooled in the secondary condenser 27, and the liquefied component 103, such as kerosene, which contains many light components is condensed and separated and stored in the light component storage tank 33. The gas components that are not condensed are sent to an exhaust gas treatment device 35, where they are treated so that they can be released into the atmosphere.

【0018】廃プラスチックの熱分解が完了した後、バ
ーナー11を消火して加熱を止め、外槽3を室温程度ま
で冷却する。熱分解の完了は、例えば、内槽1内の温度
が上昇すること等によって検知することができる。ある
いは、原料廃プラスチックの量に応じて計算量の燃料油
を得た時点で分解反応の完了と見なすようにしてもよ
い。外槽3が冷却された後、ハッチ7を開けて内槽1を
ジブクレーン5で取り出す。取り出された内槽1の残渣
105は、回転駆動軸37を有する掻き出し機39を用
いて掻き出し、洗浄する。残渣の掻き出し及び洗浄中
に、別の内槽を用いて廃プラスチックの熱分解が行われ
る。掻き出し洗浄作業を行う場所や環境は適宜選択する
ことができるので、作業者の健康を損なわないように配
慮することが容易となる。掻き出した残渣に燃料成分が
残っている場合には、この残渣を固形燃料として用いる
こともできる。
After the thermal decomposition of the waste plastic is completed, the burner 11 is extinguished, the heating is stopped, and the outer tub 3 is cooled to about room temperature. Completion of the thermal decomposition can be detected by, for example, an increase in the temperature in the inner tank 1. Alternatively, the completion of the cracking reaction may be considered when a calculated amount of fuel oil is obtained according to the amount of the raw material waste plastic. After the outer tub 3 is cooled, the hatch 7 is opened and the inner tub 1 is taken out by the jib crane 5. The taken-out residue 105 of the inner tank 1 is scraped out and washed using a scraping machine 39 having a rotary drive shaft 37. During scraping and cleaning of the residue, the waste plastic is thermally decomposed using a separate inner tank. Since the place and environment in which the scraping cleaning work is performed can be appropriately selected, it is easy to take care not to impair the health of the worker. When a fuel component remains in the scraped residue, the residue can be used as a solid fuel.

【0019】上記の熱分解装置において、内槽1の直径
dと仕切り板3aの凹部3bの内径Dとは、図3に示さ
れるように、常温においては凹部3bに嵌入された内槽
1と凹部3b表面との間にわずかの隙間ができるように
設定され、且つ、内槽1の材料の熱膨張率が仕切り板3
aの熱膨張率よりも僅かに大きくなるように素材の組合
せが選択される。このように構成することにより、常温
においては、内槽1が凹部3bに滑らかに挿入され、加
熱時には内槽1及び仕切り板3aの材料が膨張して、凹
部3bと内槽1の外表面とが密接し、内槽1への熱伝導
性が向上する。例えば、オーステナイトステンレス鋼で
内槽1を形成し、仕切り板3bを炭素鋼で形成すると、
内槽の膨張率が大きく好適に密着させることができる。
この直径比d/D(d或いはDが一定でない場合は、両
者が接触する領域での各平均値)は、0.7<d/D≦
0.98の範囲で適宜設定される。直径比が0.98以
内である方が、常温で内槽1を凹部3bに嵌入する操作
が容易であるが、0.7以下では加熱時に好適な熱伝導
性を得るのが難しくなる。
In the above-mentioned thermal decomposition apparatus, the diameter d of the inner tank 1 and the inner diameter D of the recess 3b of the partition plate 3a are, as shown in FIG. It is set so that a slight gap is formed between the surface of the concave portion 3b and the coefficient of thermal expansion of the material of the inner tank 1 is determined by the partition plate 3
The combination of materials is selected so as to be slightly larger than the coefficient of thermal expansion a. With this configuration, at normal temperature, the inner tank 1 is smoothly inserted into the recess 3b, and the material of the inner tank 1 and the partition plate 3a expands at the time of heating, so that the recess 3b and the outer surface of the inner tank 1 And the thermal conductivity to the inner tank 1 is improved. For example, when the inner tank 1 is formed of austenitic stainless steel and the partition plate 3b is formed of carbon steel,
The expansion rate of the inner tank is large, and the inner tank can be brought into close contact.
The diameter ratio d / D (when d or D is not constant, each average value in a region where both contact) is 0.7 <d / D ≦
It is set appropriately within the range of 0.98. When the diameter ratio is 0.98 or less, the operation of fitting the inner tank 1 into the concave portion 3b at normal temperature is easy, but when it is 0.7 or less, it becomes difficult to obtain a suitable thermal conductivity during heating.

【0020】加熱によって、投入したプラスチックは、
分解時の気泡による流状物の液面上昇を加味すると、概
して1.2〜1.5倍、時には2倍以上にも膨張する。
従って、廃プラスチックを内槽1一杯に収容すると、熱
分解中に内槽1から廃プラスチックが溢れる。従って、
内槽1内に廃プラスチックを収容する量は、内槽1の高
さの50〜70%とするのが好ましい。又、廃プラスチ
ックの上部を加熱すると更に上方に向かって膨らむのを
助長することになるので、熱伝導部は内槽1の下部に位
置させるのが好ましい。この点から、内槽1の軸方向高
さを凹部3bの深さの約1.2〜2倍程度に設定するの
が好ましい。
By heating, the injected plastic is
Taking into account the rise in the liquid level of the fluid due to the bubbles at the time of decomposition, the fluid generally expands 1.2 to 1.5 times, and sometimes 2 times or more.
Therefore, when the waste plastic is accommodated in one inner tank, the waste plastic overflows from the inner tank 1 during thermal decomposition. Therefore,
It is preferable that the amount of the waste plastic stored in the inner tank 1 is 50 to 70% of the height of the inner tank 1. Further, heating the upper portion of the waste plastic promotes further expansion upward, so that the heat conducting portion is preferably located at the lower portion of the inner tank 1. From this point, it is preferable to set the axial height of the inner tank 1 to about 1.2 to 2 times the depth of the recess 3b.

【0021】上記のように熱伝導部を設けることによっ
て、熱伝導性の低い空気伝導に依らず、直接、外槽から
内槽へ熱を伝達することができるので、廃プラスチック
の加熱を速く行うことができ、操作性が向上する。又、
このような燃料油を回収する廃プラスチックの熱分解操
作においては、熱伝導性が油質の向上及びばらつきの減
少にとって重要であり、加熱される廃プラスチックの占
める容積に対する熱伝導部の面積の比が0.08cm2
cm3 以上あるのが効果的である。
By providing the heat conducting section as described above, heat can be directly transmitted from the outer tank to the inner tank without relying on air conduction having low thermal conductivity, and thus the waste plastic can be heated quickly. And operability is improved. or,
In such a thermal decomposition operation of waste plastics for recovering fuel oil, thermal conductivity is important for improving oil quality and reducing dispersion, and the ratio of the area of the heat conductive portion to the volume occupied by the heated waste plastics. Is 0.08 cm 2 /
cm 3 or more certain of is effective.

【0022】従って、2重槽式の構成を採用し、熱伝導
部を設けることによって、残渣の掻き出しによる時間の
ロスを減少させ、効率よく熱供給を行うことができるた
め、プラスチックの熱分解作業に必要な作業時間を短縮
し、単位時間当たりの処理能力を上げることができる。
Therefore, by adopting the double tank type structure and providing the heat conducting portion, it is possible to reduce the time loss due to the scraping of the residue and to efficiently supply the heat. The work time required for the process can be reduced, and the processing capacity per unit time can be increased.

【0023】上述の装置において、図1に示されるよう
に、熱分解によって得た燃料をパイプ41によってバー
ナー11へ送り、燃焼に用いることができるように構成
することができる。内槽1へ廃プラスチックを入れる作
業や、残渣の掻き出し作業は、外槽と離れた場所で行っ
てもよく、適宜トラックなどの搬送手段が用いられる。
In the above-mentioned apparatus, as shown in FIG. 1, the fuel obtained by the pyrolysis can be sent to the burner 11 through a pipe 41 and used for combustion. The operation of putting the waste plastic into the inner tank 1 and the operation of scraping out the residue may be performed in a place remote from the outer tank, and a transport means such as a truck is used as appropriate.

【0024】図4は、本発明に係る熱分解装置の第2実
施例を示す。この例においては、内槽として汎用のドラ
ム缶43を用いている。この場合、凹部3bの内径部と
ドラム缶43の側部との間に空間があり、この空間は凹
部3bからドラム缶43への熱伝導性を低下させる。こ
れを改善するために、スチールウール等の金属媒体ある
いは重質油などの液状媒体を空間に充填して熱伝導部を
構成する。つまり、このような比熱の小さい充填材を介
在させることによって、内槽と密接した熱伝導部を形成
することができる。これによると、第1実施例における
d/D比が小さく加熱時の密接性が低い場合において
も、充填材を用いて補うことが可能であることが解る。
FIG. 4 shows a second embodiment of the thermal decomposition apparatus according to the present invention. In this example, a general-purpose drum 43 is used as the inner tank. In this case, there is a space between the inner diameter of the recess 3 b and the side of the drum 43, and this space reduces the thermal conductivity from the recess 3 b to the drum 43. In order to improve this, a space is filled with a metal medium such as steel wool or a liquid medium such as heavy oil to form a heat conducting portion. That is, by interposing such a filler having a small specific heat, a heat conductive portion closely contacting the inner tank can be formed. According to this, it can be understood that even when the d / D ratio in the first embodiment is small and the closeness at the time of heating is low, it is possible to compensate using the filler.

【0025】図5は、本発明に係る分解装置の第3実施
例を示す。この例においては、内槽として円錐台形の内
槽47が用いられている。従って、仕切り板3aの凹部
についても円錐台型の凹部3b’が用いられる。このよ
うに内槽及び凹部をテーパ形状にすることによって、内
槽を凹部へ移送して位置決めする操作の正確さがさほど
厳格に要求されず、凹部への嵌入作業が容易になる。内
槽及び凹部のサイズ設計において多少の誤差があって
も、加熱状態での熱伝導の不良や装置の膨張による破損
を避けられる。又、凹部に据え付けられた内槽の安定性
も得られ易い。更に、内槽の開口が広いので、残渣の取
り出しが容易である。又、図6のように、複数の内槽を
重ねて保存、運搬することができるので、内槽の保存、
運搬の際に必要な空間を少なくすることができる。
FIG. 5 shows a third embodiment of the decomposition apparatus according to the present invention. In this example, a frustoconical inner tank 47 is used as the inner tank. Therefore, a truncated cone-shaped recess 3b 'is used for the recess of the partition plate 3a. By thus forming the inner tank and the concave portion in a tapered shape, the operation of transferring the inner tank to the concave portion and positioning the same is not so strictly required, and the work of fitting into the concave portion becomes easy. Even if there is some error in the size design of the inner tank and the concave portion, it is possible to avoid poor heat conduction in the heated state and damage due to expansion of the device. In addition, the stability of the inner tank installed in the recess is easily obtained. Further, since the opening of the inner tank is wide, it is easy to take out the residue. Also, as shown in FIG. 6, a plurality of inner tanks can be stored and transported in an overlapping manner, so that the inner tanks can be stored and transported.
The space required for transportation can be reduced.

【0026】[0026]

【発明の効果】以上説明したように、本発明の廃プラス
チックの熱分解装置は、熱分解残渣の処理が行い易く分
解作業の効率が高いものであり、その工業的価値は極め
て大である。また、本発明の分解による残渣の処分も行
い易い。
As described above, the waste plastic pyrolysis apparatus of the present invention can easily treat the pyrolysis residue and has a high efficiency of the decomposition work, and its industrial value is extremely large. Further, disposal of the residue by the decomposition according to the present invention is also easy.

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

【図1】本発明に係る分解装置の第1実施例の構成を示
す概念図である。
FIG. 1 is a conceptual diagram showing a configuration of a first embodiment of a decomposition apparatus according to the present invention.

【図2】図1における外槽の内部構成を示す鉛直断面図
である。
FIG. 2 is a vertical sectional view showing an internal configuration of an outer tank in FIG.

【図3】図1における外槽の内部構成を示す水平断面図
である。
FIG. 3 is a horizontal sectional view showing the internal configuration of the outer tank in FIG.

【図4】本発明に係る分解装置の第2実施例における外
槽を示す鉛直断面図である。
FIG. 4 is a vertical sectional view showing an outer tank in a second embodiment of the decomposition apparatus according to the present invention.

【図5】本発明に係る分解装置の第3実施例のおける外
槽を示す鉛直断面図である。
FIG. 5 is a vertical sectional view showing an outer tank in a third embodiment of the decomposition apparatus according to the present invention.

【図6】図5における内槽を複数重ねた状態を示す鉛直
断面図である。
6 is a vertical sectional view showing a state in which a plurality of inner tanks in FIG. 5 are stacked.

【符号の説明】[Explanation of symbols]

1 内槽 3 外槽 9 燃焼室 11 バーナー Reference Signs List 1 inner tank 3 outer tank 9 combustion chamber 11 burner

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平6−200257(JP,A) 特開 昭57−38883(JP,A) 実開 昭61−155347(JP,U) 実開 昭60−9954(JP,U) (58)調査した分野(Int.Cl.7,DB名) C10G 1/10 ZAB B29B 17/00 C08J 11/12 ──────────────────────────────────────────────────続 き Continuation of the front page (56) References JP-A-6-200257 (JP, A) JP-A-57-38883 (JP, A) JP-A-61-155347 (JP, U) JP-A-60-155347 9954 (JP, U) (58) Fields investigated (Int. Cl. 7 , DB name) C10G 1/10 ZAB B29B 17/00 C08J 11/12

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 廃プラスチックを熱分解して燃料油を回
収する熱分解装置であって、加熱手段によって加熱され
る外槽と、外槽内に出し入れ可能な廃プラスチックを収
容するための内槽とを備え、該外槽が、加熱時に内槽表
面と密接して外槽から内槽への熱伝導性を高めるための
熱伝導部を有し、前記熱伝導部は内径Dの円筒形の仕切
り板で形成され、前記内層は直径dの円筒容器で形成さ
れるに際し、d/Dは、0.7<d/D≦0.98に設
定されることを特徴とする、廃プラスチックの熱分解装
置。
1. A pyrolysis apparatus for recovering fuel oil by pyrolyzing waste plastics, comprising: an outer tank heated by a heating means; and an inner tank for storing waste plastic that can be taken in and out of the outer tank. with the door, outer tank, close contact with the inner tank surface during heating to have the heat-conducting portion for increasing the thermal conductivity of the inner tank from the outer tank, the heat conduction part of the cylindrical inner diameter D Partition
The inner layer is formed of a cylindrical container having a diameter d.
D / D is set so that 0.7 <d / D ≦ 0.98.
A pyrolysis device for waste plastics, characterized in that:
JP33690593A 1991-12-20 1993-12-28 Waste plastic pyrolysis equipment Expired - Fee Related JP3288164B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP33690593A JP3288164B2 (en) 1993-12-28 1993-12-28 Waste plastic pyrolysis equipment
US08/262,185 US5608136A (en) 1991-12-20 1994-06-20 Method and apparatus for pyrolytically decomposing waste plastic
DE4446964A DE4446964C2 (en) 1993-12-28 1994-12-28 Method and device for the pyrolytic decomposition of plastic waste
US09/033,921 US6172275B1 (en) 1991-12-20 1998-03-03 Method and apparatus for pyrolytically decomposing waste plastic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP33690593A JP3288164B2 (en) 1993-12-28 1993-12-28 Waste plastic pyrolysis equipment

Publications (2)

Publication Number Publication Date
JPH07197032A JPH07197032A (en) 1995-08-01
JP3288164B2 true JP3288164B2 (en) 2002-06-04

Family

ID=18303728

Family Applications (1)

Application Number Title Priority Date Filing Date
JP33690593A Expired - Fee Related JP3288164B2 (en) 1991-12-20 1993-12-28 Waste plastic pyrolysis equipment

Country Status (2)

Country Link
JP (1) JP3288164B2 (en)
DE (1) DE4446964C2 (en)

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TW386052B (en) * 1995-08-17 2000-04-01 Shinagawa Fuel Co Ltd Pyrolytic reactor for waste plastic
US5837037A (en) * 1996-07-17 1998-11-17 Texaco Inc Gas handling for plastics liquefaction
DE69809310T2 (en) * 1997-02-24 2003-03-20 Meidensha Tokio Tokyo Kk Process and system for removing pollutants
US5902915A (en) * 1997-03-20 1999-05-11 Lawrence Plasma Research Laboratory Inc. Process for producing liquid hydrocarbons
DE10003221B4 (en) * 2000-01-26 2010-08-26 Volkswagen Ag Process for the thermal utilization of hydrocarbons
JP2003286490A (en) * 2002-03-28 2003-10-10 Yutaka Abe Method and system for dry distillation of rubber tire and the like into oil, and apparatus for dry distillation of rubber tire and the like
TW201100471A (en) * 2009-06-18 2011-01-01 xie-sen Wu Method for pyrolyzing organic polymer to classify and recycle substrate and apparatus thereof
CN101693844B (en) * 2009-10-16 2012-10-10 江南大学 Method for liquefying plant biomass and waste polyester mixed supercritical fluid
DE102010041033A1 (en) * 2010-09-20 2012-03-22 Siemens Aktiengesellschaft Material utilization with electropositive metal
CN106118707B (en) * 2016-07-28 2017-10-27 徐效奇 Waste plastics innocent treatment equipment and method
DE102020104763B3 (en) * 2020-02-24 2021-05-27 emma technologies GmbH Hydrogen pyrolysis system arrangement
CN113462421B (en) * 2021-07-30 2023-03-28 重庆大学 Pyrolysis method for heating medical waste or waste plastic by molten salt

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FR2223448B1 (en) * 1973-03-31 1977-06-17 Sumitomo Shipbuild Machinery
JPS5738883A (en) * 1980-08-18 1982-03-03 Seitaro Noro Retort for waste
JPS609954U (en) * 1983-06-28 1985-01-23 三上 順一 Tire external heating carbonization furnace
JPS6226435Y2 (en) * 1985-03-13 1987-07-07
DE4243063C2 (en) * 1991-12-20 1996-01-11 Toshiba Kawasaki Kk Method and device for the pyrolytic decomposition of plastic, in particular plastic waste
DE4207976C2 (en) * 1992-03-13 2001-03-15 Rwe Umwelt Ag Process for the production of olefins by thermal treatment of plastic waste
JPH06200257A (en) * 1992-11-16 1994-07-19 Muneharu Ueda Apparatus for treating petroleum-derived polymer article
DE4344311A1 (en) * 1993-12-23 1995-06-29 Linde Ag Process and device for the thermal depolymerization of plastics

Also Published As

Publication number Publication date
DE4446964A1 (en) 1995-06-29
DE4446964C2 (en) 2002-07-04
JPH07197032A (en) 1995-08-01

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