JPH05245463A - Treatment of mixed plastic waste and device therefor - Google Patents

Treatment of mixed plastic waste and device therefor

Info

Publication number
JPH05245463A
JPH05245463A JP29770891A JP29770891A JPH05245463A JP H05245463 A JPH05245463 A JP H05245463A JP 29770891 A JP29770891 A JP 29770891A JP 29770891 A JP29770891 A JP 29770891A JP H05245463 A JPH05245463 A JP H05245463A
Authority
JP
Japan
Prior art keywords
mixed plastic
plastic waste
thermal decomposition
gas
temperature
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.)
Granted
Application number
JP29770891A
Other languages
Japanese (ja)
Other versions
JP2648412B2 (en
Inventor
Kiyoshi Saito
喜代志 斎藤
Satoshi Suzuki
智 鈴木
Hiroyuki Nakatani
裕之 中谷
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.)
Fuji Tetsuku Kk
FUJITETSUKU KK
National Institute of Advanced Industrial Science and Technology AIST
Original Assignee
Fuji Tetsuku Kk
FUJITETSUKU KK
Agency of Industrial Science and Technology
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 Fuji Tetsuku Kk, FUJITETSUKU KK, Agency of Industrial Science and Technology filed Critical Fuji Tetsuku Kk
Priority to JP29770891A priority Critical patent/JP2648412B2/en
Publication of JPH05245463A publication Critical patent/JPH05245463A/en
Application granted granted Critical
Publication of JP2648412B2 publication Critical patent/JP2648412B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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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
    • 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
    • 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)
  • Processing Of Solid Wastes (AREA)
  • Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Coke Industry (AREA)

Abstract

PURPOSE:To remove chlorine from a treated mixed plastic waste completely and thereby, recover high-purity hydrogen chloride by crushing the mixed plastic waste, then increasing the temperature stepwise until the highest attainable temperature level within a specified temperature range for thermal decomposition is attained separating the gas product from a fused solid. CONSTITUTION:A thermal decomposition reaction device 1 consists of a reaction cylinder 4 of corrosion-inhibitive material, thermocouples 5-1 to 5-3, a hopper 6, an opposite-direction rotating two-axial screw 7, an adjustment valve 10, a gas intake tube 11, and a fused solid outflow tube 12. A mixed plastic material is charged from the hopper 6. The temperature is increased stepwise using a heater 2 and monitoring it using the thermocouples 5-1 to 5-3 so that the highest attainable temperature level is 290 to 330 deg.C within a range up to 330 deg.C from a normal temperature. In addition, the mixed plastic material is stirred and mixed using an opposite-direction rotating two-axial screw 7 to cause a thermal decomposition. Further, the decomposed molten product and a decomposition gas are discharged by adjusting an outflow pressure using an adjustment valve 10. Consequently, the gas is separately recovered by an HCl recovery vessel 13 through a suction tube 11 and the decomposed molten product by a solid outflow tube 12, respectively.

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、混合プラスチツク廃棄
物を減容化、熱分解油化及び焼却など無公害に再資源化
を行うための前処理に関し、該試料から予め腐食性の塩
素を実質的に除去するための熱分解法及び処理装置に関
する。
BACKGROUND OF THE INVENTION The present invention relates to a pretreatment for reducing the volume of a mixed plastic waste, recycling it into a pollution-free oil, and incinerating it in a pollution-free manner. It relates to a pyrolysis method and a treatment device for substantially removing.

【0002】[0002]

【従来の技術】日本の場合、近年のプラスチツク原材料
生産量は、ポリオレフイン系プラスチツク(例えばポリ
エチレン、ポリプロピレン)が約37.0%、ポリ塩化
ビニル(PVC)系プラスチツクが約17.0%及びポ
リスチレン系プラスチツクが約12.0%と、これらの
熱可塑性プラスチツクが上位を占めており、プラスチツ
ク総生産量の約66.0%を占めている。
2. Description of the Related Art In Japan, the production amount of plastic raw materials in recent years is about 37.0% for polyolefin type plastics (eg polyethylene, polypropylene), about 17.0% for polyvinyl chloride (PVC) type plastics and polystyrene type. Plastics account for about 12.0%, and these thermoplastics account for the top, accounting for about 66.0% of the total plastic production.

【0003】一方、使用耐久年数を過ぎて廃棄されるプ
ラスチツク類は、混合プラスチツク廃棄物となつて排出
され、その廃棄量も年々増加している。
On the other hand, plastics discarded after the end of their useful life are discharged as mixed plastic wastes, and the amount of disposal is increasing year by year.

【0004】混合プラスチツク廃棄物の内訳は、家庭な
どからの一般廃棄物と生産、加工工場などからの産業廃
棄物に分類される。これらの混合プラスチツク廃棄物の
処理方法は、ごく限られた良質な種類を選別し、成形品
などに加工して再利用を行つているが、ほとんどが埋め
立てているか、焼却処分を行つているにすぎない。
The breakdown of mixed plastic waste is classified into general waste from households and industrial waste from production and processing plants. Regarding the treatment method of these mixed plastic wastes, very limited types of high quality are selected, processed into molded articles and reused, but most of them are landfilled or incinerated. Only.

【0005】しかし、年々増大する混合プラスチツク廃
棄物は、埋め立てる場所の確保が困難となり、その対応
が急がれている。この際、埋め立てる場所の問題点を早
急に解決するためには、混合プラスチツク廃棄物を焼却
処分を行うべきと考えられる。しかし、混合プラスチツ
ク廃棄物中には、塩素系プラスチツクが混入しているた
め、焼却により塩素分がHClに変換して排ガス中に混
入することにより、焼却炉、配管の劣化や腐食が促進さ
れる。さらにHClを含んだ排ガスがそのまま大気中に
飛散された場合には、生物や自然環境に悪い影響を引き
起こす原因となる。
However, it is difficult to secure a landfill site for mixed plastic waste, which is increasing year by year, and there is an urgent need to deal with it. At this time, in order to quickly solve the problem of the landfill site, it is considered necessary to incinerate the mixed plastic waste. However, since chlorine plastics are mixed in the mixed plastic waste, chlorine content is converted to HCl by incineration and mixed in the exhaust gas, which promotes deterioration and corrosion of the incinerator and piping. .. Further, if the exhaust gas containing HCl is scattered into the atmosphere as it is, it may cause a bad influence on living things and the natural environment.

【0006】従来、混合プラスチツク廃棄物からのHC
l除去技術は、熱分解反応又は焼却などにおいて高温で
処理した後、生成ガス中のHClを湿式法及び乾式法で
除去している。湿式法は、主にアルカリ洗浄を行つてお
り、HCl除去率が高いが、廃水処理、除去装置及び維
持管理に多額の費用を要する。乾式法では、反応炉内に
直接アルカリ物質を噴霧する方法、移動層法などがある
が、湿式法よりHCl除去率が低い。このように従来の
HCl除去方法は、反応炉内が高温下で生成したHCl
にさらされるため腐食が一段と進行して破損が著しく、
対策が急がれている。一方混合プラスチツク廃棄物から
PVC系プラスチツクを完全に分別することは不可能で
ある。
Conventionally, HC from mixed plastic waste
The l removal technology removes HCl in the produced gas by a wet method and a dry method after treating at a high temperature in a thermal decomposition reaction or incineration. The wet method mainly performs alkaline cleaning and has a high HCl removal rate, but requires a large amount of cost for wastewater treatment, removal equipment and maintenance. The dry method includes a method of directly spraying an alkaline substance into the reaction furnace and a moving bed method, but the removal rate of HCl is lower than that of the wet method. As described above, the conventional method for removing HCl is that HCl generated in the reaction furnace at high temperature is
Corrosion progresses further because it is exposed to
Measures are urgently needed. On the other hand, it is impossible to completely separate PVC-based plastics from mixed plastic wastes.

【0007】そのために、PVC系プラスチツクの特異
な熱特性を利用して、前処理で無公害にHClとして除
去することは装置の腐食、大気汚染、脱HClした融解
固体物の再資源化、HClの再利用及び処理コストなど
の面で最も得策な処理方法と考えられる。
[0007] Therefore, by utilizing the peculiar thermal characteristics of PVC-based plastics, it is possible to remove as pollution-free HCl as pretreatment by means of equipment corrosion, air pollution, recycling of dehydrochlorinated molten solids, and HCl. It is considered to be the best method in terms of reuse and processing cost.

【0008】[0008]

【発明が解決しようとする課題】混合プラスチツク廃棄
物からPVC系プラスチツク(PVC)を選別し排除し
ようとしても完全な分別は不可能である。ここで、混合
プラスチツク廃棄物中のHClを効率的に除去するため
には、PVC系プラスチツクの熱特性を把握して、熱的
な性質に沿つた脱HClの方法を検討する必要がある。
Even if PVC-based plastics (PVC) are selected and excluded from mixed plastic wastes, complete separation is impossible. Here, in order to efficiently remove HCl in the mixed plastic waste, it is necessary to grasp the thermal characteristics of the PVC plastic and study the method of de-HCl according to the thermal properties.

【0009】そこで本発明の第1の目的は、HClを無
公害に処理するため、混合プラスチツク廃棄物を、減容
化、熱分解油化及び焼却などの処理を行う以前に、予め
該試料から有害なHClガスを除去する方法及び前処理
熱分解装置を提供することにある。
Therefore, the first object of the present invention is to treat HCl without pollution, so that the mixed plastic waste is treated in advance from the sample before the treatment such as volume reduction, pyrolysis oil conversion and incineration. It is to provide a method for removing harmful HCl gas and a pretreatment thermal decomposition apparatus.

【0010】本発明の第2の目的は、混合プラスチツク
廃棄物中のPVC系プラスチツクが熱分解してHClガ
スのみが生成する条件下で前処理し、簡易な方法で脱H
Clする方法及びその装置を提供しようとするものであ
る。すなわち、混合プラスチツク廃棄物を前処理段階で
熱分解して脱HCl化を行うことにより、公害防止を前
提とした実用的な処理条件による減容化、熱分解油化及
び焼却などの資源の有効利用を効率的に行うための基本
的な手段を提供するものである。
A second object of the present invention is to pretreat the PVC plastic in the mixed plastic waste by thermal decomposition to generate only HCl gas, and dehydrogenate by a simple method.
The present invention intends to provide a Cl method and an apparatus therefor. In other words, by thermally decomposing the mixed plastic waste in the pre-treatment stage and de-HCling it, effective treatment of resources such as volume reduction, pyrolysis oil conversion and incineration by practical treatment conditions assuming pollution prevention. It provides the basic means for efficient use.

【0011】本発明の他の目的は混合プラスチツク廃棄
物中のPVC系プラスチツクが熱分解して発生するHC
lを極めて高純度に回収し、再利用可能な純度及び濃度
で得ること方法及び処理装置を提供することにある。
Another object of the present invention is HC generated by thermal decomposition of PVC plastic in mixed plastic waste.
It is an object of the present invention to provide a method and a processing apparatus for recovering 1 with extremely high purity and obtaining it in reusable purity and concentration.

【0012】[0012]

【課題を解決するための手段】本発明者らの研究によれ
ば、前記本発明の目的は混合プラスチツク廃棄物を粉砕
してなる試料を、そのまゝ或いは脱水した後、常温から
330℃の範囲でしかも最高到達温度が290〜330
℃となるように段階的に昇温熱分解し、しかる後ガス生
成物と融解固体物に分離することを特徴とする塩素が実
質的に除去され且つ減容化された混合プラスチツク廃棄
物処理物を得るための処理方法によつて達成され、さら
に本発明の目的は、 a) 混合プラスチツク廃棄物を粉砕してなる試料を段
階的に昇温熱分解を行うための外部加熱を有する熱分解
反応装置、 b) 前記熱分解反応装置内に設置された反応筒に試料
を供給するためのホツパー、 c) 前記熱分解反応装置の反応筒内に試料を挿入する
異方向回転式二軸スクリユー、 d) 前記熱分解反応装置の反応筒出口側に加熱溶融し
た生成物を均一に混合する空間部分の反応室と流出圧力
を調整する調整バルブ e) 前記熱分解反応装置の反応筒出口の調整バルブか
ら流出するガス生成物と融解固体物とを分離するための
分離器及び f) ガス生成物からHClを回収するため回収器より
なる混合プラスチツク廃棄物の処理装置によつて達成さ
れることが見出された。
According to the research conducted by the present inventors, the object of the present invention is to obtain a sample obtained by pulverizing mixed plastic wastes as it is, or after dehydration, from room temperature to 330 ° C. The highest temperature reached in the range is 290-330
A mixed plastic waste treatment product in which chlorine is substantially removed and the volume is reduced, which is characterized in that it is thermally decomposed at a temperature gradually increasing to ℃, and then separated into a gas product and a molten solid substance. A further object of the present invention, which is achieved by a treatment method for obtaining a) is: a) a pyrolysis reactor having external heating for stepwise thermal decomposition of a sample obtained by pulverizing mixed plastic waste, b) a hopper for supplying a sample to a reaction tube installed in the thermal decomposition reactor, c) a counter-rotating biaxial screw for inserting a sample into the reaction tube of the thermal decomposition reactor, d) the above The reaction chamber in the space where the heated and melted product is evenly mixed on the outlet side of the reaction tube of the thermal decomposition reaction device and the adjusting valve for adjusting the outflow pressure e) Outflow from the adjusting valve at the outlet of the reaction tube of the thermal decomposition reaction device Gas production It has been found to be achieved by means of a mixed plastics waste treatment unit comprising a separator for separating the product and molten solids and f) a collector for recovering HCl from the gas product.

【0013】かゝる本発明によれば、混合プラスチツク
廃棄物から、実質的に塩素を含有しないプラスチツク融
解物が得られ、しかも処理前と比べて約1/6〜1/1
5に減容化することができ、そのまゝ廃棄または埋め立
てることが容易であるばかりでなく、燃料として使用し
ても充分に利用できるものである。
According to the present invention, a plastic melt substantially free of chlorine is obtained from the mixed plastic waste, and the melt is about 1/6 to 1/1 as compared with that before the treatment.
It is possible to reduce the volume to 5, and it is not only easy to dispose of or to bury it, but also it can be sufficiently used as a fuel.

【0014】さらに本発明によればPVC系プラスチツ
クから熱分解して発生したHClが大気中に排出されず
に回収可能であり、その上HClが高純度で回収される
からその再利用が期待できる。
Further, according to the present invention, HCl generated by thermal decomposition of PVC plastic can be recovered without being discharged into the atmosphere, and since HCl is recovered in high purity, its reuse can be expected. ..

【0015】以下本発明についてさらに詳細に説明す
る。
The present invention will be described in more detail below.

【0016】PVC系プラスチツクを不活性ガス中で加
熱すると特異な重量減少曲線を描くことが知られてい
る。ここで重量減少は、230℃以上で現れ、360℃
までの第1ゾーンと、360℃から420℃の第2ゾー
ン及び420℃から500℃までの第3ゾーンが観察す
ることができる。
It is known that when PVC-based plastics are heated in an inert gas, a unique weight loss curve is drawn. Here, the weight loss appears above 230 ° C and 360 ° C.
The first zone up to, the second zone from 360 ° C to 420 ° C, and the third zone from 420 ° C to 500 ° C can be observed.

【0017】第1ゾーンの重量減少は、ほぼ塩素分が脱
離し、分解反応してHClが放出される。
Regarding the weight reduction in the first zone, almost all chlorine is desorbed and the decomposition reaction is carried out to release HCl.

【0018】さらに、360℃以上の高温度側では、C
−C結合の開裂による各種低級炭化水素やそれらの誘導
体が生成する。
Further, on the high temperature side above 360 ° C., C
Various lower hydrocarbons and their derivatives are produced by cleavage of the -C bond.

【0019】すなわち、混合プラスチツク廃棄物から如
何に前処理で、HClのみを除去することがポイントで
ある。PVC系プラスチツクは、常圧で230℃から3
60℃に加熱するとHClを発生するが、この温度領域
で完全に塩素分を除去することは非常に困難である。
That is, the point is to remove only HCl from the mixed plastic waste by pretreatment. PVC-based plastics can be heated from 230 ° C to 3 at normal pressure.
When heated to 60 ° C., HCl is generated, but it is very difficult to completely remove chlorine in this temperature range.

【0020】本発明は、一般廃棄物や産業廃棄物中から
分別収集した混合プラスチツク廃棄物を対象にして、簡
易な処理方法において脱HCl化することにより、次の
減容化、熱分解油化及び焼却などの処理対策のための適
正な情報を提供するものである。
The present invention is intended for mixed plastic wastes that are separately collected from general wastes and industrial wastes, and dehydrochlorination is performed by a simple treatment method to reduce the volume and to make pyrolysis oil. It also provides appropriate information for disposal measures such as incineration.

【0021】本発明に適用する混合プラスチツク廃棄物
は、混合物であればいずれでもよいが共重合体などでも
好ましい。また、混合プラスチツク廃棄物は、平均粒径
約20mm以下、好ましくは10mm以下に粉砕した物
であればフイルム状、シート状又は成型品などの形状に
関係なく用いられる。
The mixed plastic waste used in the present invention may be any mixture as long as it is a mixture, but a copolymer or the like is also preferable. Further, the mixed plastic waste can be used regardless of the shape such as a film, a sheet or a molded product as long as it is a crushed product having an average particle size of about 20 mm or less, preferably 10 mm or less.

【0022】処理対策に関連して本発明の作用を説明す
る。まず、混合プラスチツク廃棄物をそのまま又は脱水
後、外部加熱を有する熱分解反応装置に設置しているホ
ツパーに投入し、その反応筒内では試料が異方向回転式
二軸スクリユーで常温から挿入されて反応筒内で段階的
に320℃の範囲まで均一な混合と流出圧力の調整を受
けて熱分解したHClに富むガス生成物と融解固体物の
混合物が流出される。その他の多量を占めるポリエチレ
ン、ポリプロピレン及びポリスチレンなどの汎用プラス
チツクは、約370℃以上でなければ気化しないという
熱特性の違いがあり、これら異種のプラスチツクは混合
されても、熱特性が併合せず、本来の特性をそのまま保
持している。
The operation of the present invention will be described in relation to processing measures. First, the mixed plastic waste, as it is or after dehydration, is put into a hopper installed in a thermal decomposition reactor having external heating, and the sample is inserted from room temperature in the reaction cylinder by a bi-directional rotating screw screw. In the reaction tube, a mixture of a gas product rich in HCl and a molten solid pyrolyzed under the uniform mixing and the adjustment of the outflow pressure in stages up to 320 ° C. is discharged. Other general-purpose plastics such as polyethylene, polypropylene, and polystyrene, which occupy a large amount, have a difference in thermal property that they do not vaporize unless they are about 370 ° C. or higher. Even if these different kinds of plastics are mixed, thermal properties are not combined, It retains its original characteristics.

【0023】このため、320℃以下での熱分解は、P
VC系プラスチツクから脱HClが選択的に生起し、純
度98.6%以上のものが得られ、用途の活性も十分に
可能である。
Therefore, the thermal decomposition at 320 ° C. or lower is P
Dehydrochlorination selectively occurs from VC plastics, and a purity of 98.6% or more is obtained, and the activity for use is sufficiently possible.

【0024】また流出した融解固体物は、減容化される
と共に脱HCl化されるため、熱分解油化又は燃料など
の資源として再利用と公害防止に役立つことができる。
このように本発明は、混合プラスチツク廃棄物を前処理
で脱HCl化して減容化した融解固体物が得れる基本的
な一連の処理方法とその処理装置を提供するものであ
る。
Further, the melted solid matter that has flown out is reduced in volume and dehydrochlorinated, so that it can be used as a resource for pyrolysis oil conversion or fuel, etc., and can be useful for recycling and pollution prevention.
As described above, the present invention provides a basic series of treatment methods and a treatment apparatus for obtaining a molten solid substance having a reduced volume by dehydrochlorination of mixed plastic waste in a pretreatment.

【0025】以下、本発明の方法及びその装置を添付図
面に基づいて説明する。図1は本発明の装置の正面の概
略図、図2は平面の概略図、図3は右側面の概略図であ
る。図1の正面図において、熱分解反応装置(1)は、
加熱ヒーター(2)、温度調節器(3)、前記加熱ヒー
ター(2)で覆いされている円筒形の反応筒(4)、反
応筒(4)内に挿入されている熱電対(5−1、5−
2、5−3)、反応筒(4)の上部に設置し、試料を供
給するためのホツパー(6)、反応筒(4)内に試料を
導入する異方向回転式二軸スクリユー(7)、異方向回
転式二軸スクリユー(7)に連結して回転数を調節する
電機モーター(8)、反応筒(4)の出口側に加熱溶融
した生成物を均一に混合する反応室(9)と流出圧力を
調整する調整バルブ(10)及び生成物の内、ガス成分
のみを吸入するガス吸入管(11)、融解固体物のみを
流出する融解固体物流出管(12)から構成されてい
る。
The method and apparatus of the present invention will be described below with reference to the accompanying drawings. 1 is a schematic front view of the apparatus of the present invention, FIG. 2 is a schematic plan view, and FIG. 3 is a schematic right side view. In the front view of FIG. 1, the thermal decomposition reaction device (1) is
A heater (2), a temperature controller (3), a cylindrical reaction tube (4) covered with the heater (2), and a thermocouple (5-1) inserted in the reaction tube (4). , 5-
2, 5-3), a hopper (6) installed on top of the reaction tube (4) to supply the sample, and a bidirectional rotation type twin screw screw (7) for introducing the sample into the reaction tube (4). An electric motor (8) connected to a bi-directional screw type screw (7) for adjusting the rotation speed, and a reaction chamber (9) for uniformly mixing the heated and melted product at the outlet side of the reaction tube (4). And a regulating valve (10) for regulating the outflow pressure, a gas suction pipe (11) for inhaling only the gas component of the product, and a molten solids outflow pipe (12) for outflowing only the molten solids. ..

【0026】熱分解反応装置(1)において、反応筒
(4)の上部に設置されたホツパー(6)からは、好ま
しくは粒径10.0mm以下に粉砕した混合プラスチツ
ク廃棄物が投入され、反応筒(4)内の異方向回転式二
軸スクリユー(7)で試料が導入される。異方向回転式
二軸スクリユー(7)で導入された試料は、反応筒
(4)の外周を加熱ヒーター(2)の電気回路中に接続
された温度調節器(3)で常温から330℃の範囲ま
で、最高到達温度が290℃〜330℃となるように段
階的に加熱され熱分解される。ここで、熱電対(5−
1)、(5−2)及び(5−3)は、各々独立して温度
制御を行つており熱電対(5−3)の領域が最高到達温
度となる。最高到達温度の好ましい温度は300〜32
0℃の範囲である。本発明において混合プラスチツク廃
棄物の粉砕試料を、段階的に前記最高到達温度まで加熱
することが目的達成のために必要である。段階的とは常
温から最高到達温度まで次第に温度を上昇させながら加
熱する操作である。具体的には約8〜62℃/分、好ま
しくは32〜55℃/分の上昇速度で加熱し、全加熱時
間が約4分〜約30分好ましくは約4分〜約10分とな
るように制御することが有利である。
In the thermal decomposition reactor (1), a mixed plastic waste crushed to preferably a particle size of 10.0 mm or less is charged from a hopper (6) installed on the upper part of the reaction tube (4) to carry out the reaction. The sample is introduced by the counter-rotating biaxial screw (7) in the cylinder (4). The sample introduced by the counter-rotating twin-screw screw (7) was heated from room temperature to 330 ° C. by the temperature controller (3) connected to the outer circumference of the reaction tube (4) in the electric circuit of the heater (2). Up to the range, it is heated stepwise so that the highest temperature reaches 290 ° C to 330 ° C and is pyrolyzed. Here, the thermocouple (5-
1), (5-2) and (5-3) each independently perform temperature control, and the region of the thermocouple (5-3) has the highest attainable temperature. The preferred maximum temperature is 300 to 32
It is in the range of 0 ° C. In the present invention, it is necessary to heat the crushed sample of the mixed plastic waste in stages to the above-mentioned maximum temperature for the purpose. The stepwise operation is an operation of gradually increasing the temperature from room temperature to the highest temperature. Specifically, heating is performed at a rising rate of about 8 to 62 ° C./min, preferably 32 to 55 ° C./min so that the total heating time is about 4 minutes to about 30 minutes, preferably about 4 minutes to about 10 minutes. It is advantageous to control

【0027】この処理による溶融生成物は反応筒(4)
の出口側にある反応室(9)で均一に混合され、さらに
調整バルブ(10)で流出圧力を調整することにより、
分離室内において、ガス成分と融解固体物に分離され、
それぞれガス吸入管(11)、融解固体物流出管(1
2)へと導かれる。
The molten product obtained by this treatment is the reaction tube (4).
By uniformly mixing in the reaction chamber (9) on the outlet side of the, and adjusting the outflow pressure with the adjusting valve (10),
In the separation chamber, it is separated into gas components and molten solids,
Gas suction pipe (11), molten solids outflow pipe (1
It leads to 2).

【0028】HCl回収器(13)は、前記熱分解反応
装置(1)の出口側ガス吸入管(11)に接続された吸
引ポンプ(14)、吸収塔(15)、噴霧管(16)、
吸収塔(15)内の充填物(17)、吸収液の抜き出し
管(18)及び微少ガスの吸着塔(19)から成つてい
る。
The HCl recovery unit (13) is equipped with a suction pump (14) connected to the outlet side gas suction pipe (11) of the thermal decomposition reaction apparatus (1), an absorption tower (15), a spray pipe (16),
It comprises a packing (17) in the absorption tower (15), a withdrawal pipe (18) for absorbing liquid, and an adsorption tower (19) for minute gas.

【0029】HCl回収器(13)では、吸引ポンプ
(14)により吸引塔(15)の底部から塔頂に向つて
上昇するHClが、塔頂部に設けている噴霧管(16)
から水が霧状になつて吸収塔(15)内を降下する。ま
た、吸収塔(15)内には水とHClの接触を良くする
ために充填物(17)を有している。吸収塔(15)を
降下する水と底部から上昇するHClは、接触して水に
吸収されて塩酸として吸収塔(15)の塔底に溜まり、
抜き出し管(18)により回収される。微少の有害ガス
はさらに吸着塔(19)を通過して完全に吸着される。
In the HCl recovery unit (13), HCl rising by the suction pump (14) from the bottom of the suction tower (15) toward the top of the tower is a spray pipe (16) provided at the top of the tower.
The water then becomes mist and descends in the absorption tower (15). In addition, a packing (17) is provided in the absorption tower (15) to improve contact between water and HCl. The water descending the absorption tower (15) and the HCl rising from the bottom come into contact with each other and are absorbed by the water to accumulate as hydrochloric acid at the bottom of the absorption tower (15).
It is collected by the withdrawal pipe (18). The minute harmful gas further passes through the adsorption tower (19) and is completely adsorbed.

【0030】[0030]

【実施例】次に、この発明に係る混合プラスチツク廃棄
物中の減容化と脱HClの熱分解反応装置(1)を用い
て処理した実験結果について説明する。
EXAMPLES Next, the experimental results of processing using the thermal decomposition reaction apparatus (1) for volume reduction and dehydrochlorination in mixed plastic waste according to the present invention will be described.

【0031】実施例 本実施例で使用した熱分解反応装置は、第1図に示した
熱分解反応装置(1)において、反応筒(4)、熱電対
(5−1、5−2、5−3)、ホツパー(6)、異方向
回転式二軸スクリユー(7)、調整バルブ(10)、ガ
ス吸入管(11)及び融解固体物流出管(12)は、耐
腐食性の素材(たとえばSUS27又はSUS32鋼
製)であつて、図示と同様の構造を有し、反応筒(4)
の長さが300mm、内径が26mm(2個)の内に、
スクリユーの長さが275mm、直径が14mm(2
本)、スクリユーに均一な間隔に翼が収めており、反応
筒(4)の空間容積が0.2lのものを用いた。
Example The thermal decomposition reaction apparatus used in this example is the same as the thermal decomposition reaction apparatus (1) shown in FIG. 1, except that the reaction tube (4) and the thermocouples (5-1, 5-2, 5) are used. -3), the hopper (6), the counter-rotating biaxial screw (7), the regulating valve (10), the gas suction pipe (11) and the molten solids outflow pipe (12) are made of a material resistant to corrosion (for example, (Made of SUS27 or SUS32 steel) having the same structure as that shown in the drawing, and a reaction tube (4)
Within the length of 300 mm and the inner diameter of 26 mm (2 pieces),
The length of the screen is 275 mm and the diameter is 14 mm (2
), The blades were housed in the screen at even intervals, and the reaction cylinder (4) had a space volume of 0.2 liter.

【0032】熱分解温度は、常温から段階的に昇温さ
せ、その最高到達温度を260℃から320℃と種々に
代え、またPVCの混合割合を変えた混合プラスチツク
廃棄物の脱HCl状態を調べた。生成した融解固体物生
成物の残留HCl濃度の分析は、試料量10gを回分式
熱分解装置で常温から500℃まで等速昇温して熱分解
させ、ガス生成物、油生成物及び残留物に分離し、ガス
生成物中のHCl濃度をガスクロマトグラフイーとHC
l検知管で測定した。
The thermal decomposition temperature was raised stepwise from room temperature, the maximum temperature was changed from 260 ° C. to 320 ° C., and the dehydrochlorination state of the mixed plastic waste in which the mixing ratio of PVC was changed was examined. It was The analysis of residual HCl concentration of the produced molten solid product was conducted by heating a sample amount of 10 g at a constant rate from room temperature to 500 ° C. in a batch pyrolysis apparatus to pyrolyze it, thereby producing a gas product, an oil product and a residue. And the HCl concentration in the gas product was separated by gas chromatography and HC.
1 It was measured with a detector tube.

【0033】使用した試料;試料には、高密度ポリエチ
レン、低密度ポリエチレン、ポリプロピレンが混合して
いる産業廃棄物(PE・PP)と一般廃棄物から分別し
た玉子ケース(PVC)を用いた。PE・PPとPVC
の混合物の脱HCl熱分解処理には、試料量0.32〜
1.70kg/hrとした。これらの試料については、
種々の条件で脱HClした融解固体生成物の残留HCl
の分析結果を次に示す。
Samples used: As the sample, an industrial waste (PE / PP) mixed with high density polyethylene, low density polyethylene and polypropylene and an egg case (PVC) separated from general waste were used. PE / PP and PVC
For dehydrochlorination treatment of the mixture of
It was 1.70 kg / hr. For these samples,
Residual HCl of molten solid product de-HCled under various conditions
The analysis results of are shown below.

【0034】使用したPVCのみを回分式熱分解装置で
常温から500℃まで等速昇温して熱分解させ、生成し
たガス生成中のHCl濃度は、57.6wt%であり、
油生成物中に溶解しているHCl濃度は、微量であつ
た。また残留物中のHCl濃度は検出されなかつた。
Only the PVC used was heated at a constant rate from room temperature to 500 ° C. in a batch pyrolysis apparatus to be pyrolyzed, and the HCl concentration in the produced gas was 57.6 wt%.
The concentration of HCl dissolved in the oil product was very small. Also, no HCl concentration was detected in the residue.

【0035】[1] 昇温熱分解温度によるHClの除
去割合;表1は、本発明装置でPE・PPにPVCを
9.0wt%に混合し、処理量を一定にした場合、常温
から段階的昇温した熱分解温度260〜320℃におけ
るHClの除去割合の分析結果を示すものである。
[1] Removal of HCl by heating pyrolysis temperature
Removed by the ratio; Table 1, the PVC to PE · PP in the present invention apparatus is mixed with 9.0 wt%, when the processing amount constant, the HCl in the thermal decomposition temperature of two hundred and sixty to three hundred twenty ° C. then allowed stepwise elevated from room It shows the analysis result of the removal rate.

【0036】[0036]

【表1】 表1より、本発明装置によるHClの除去割合は、処理
量が0.32kg/hrと少ない場合、段階的な昇温の
最高温度260℃から300℃でもHClの除去割合に
変化がなく高い除去割合を示した。処理量が上記の約
3.8倍になると、300℃以上の昇温の最高温度から
高いHClの除去割合であることを確認した。
[Table 1] According to Table 1, the removal rate of HCl by the device of the present invention is high and the removal rate of HCl does not change even when the maximum temperature of the stepwise temperature increase from 260 ° C. to 300 ° C. is high when the treatment amount is as low as 0.32 kg / hr. The percentage is shown. It was confirmed that when the treatment amount was about 3.8 times the above, the removal rate of HCl was high from the maximum temperature of 300 ° C. or higher.

【0037】[2] PVCの混合割合とHClの除去
割合;
[2] Mixing ratio of PVC and removal of HCl
Ratio;

【0038】[0038]

【表2】 表2には、PE・PPにPVCを5.0wt%から15.
0wt%の範囲で混合し、常温から段階的に昇温熱分解
した最高温度を300℃と320℃とにおいて、処理量
を1.12〜1.92kg/hrとした場合のHClの除
去割合の分析結果と滞留時間の結果を示すものである。
[Table 2] Table 2 shows that PE / PP with PVC from 5.0 wt% to 15.
Analysis of the removal rate of HCl when mixed in the range of 0 wt% and thermally decomposed gradually from room temperature at the maximum temperatures of 300 ° C. and 320 ° C. and the treatment amount of 1.12 to 1.92 kg / hr. The results and the results of residence time are shown.

【0039】本発明の熱分解装置による滞留時間は次の
ように求めた。
The residence time by the thermal decomposition apparatus of the present invention was determined as follows.

【0040】[0040]

【数1】 表2より、PVCの混合割合が15.0wt%であつて
も、段階的に昇温熱分解する最高温度が300〜320
℃の比較的低温下であつても、99.9wt%以上の高
いHClの除去割合であることを確認した。
[Equation 1] From Table 2, even if the mixing ratio of PVC is 15.0 wt%, the maximum temperature for stepwise thermal decomposition is 300 to 320.
It was confirmed that the removal rate of HCl was as high as 99.9 wt% or more even at a relatively low temperature of ℃.

【0041】また、HClを除去する滞留時間は4.5
〜8.7分と短時間であることも確認した。
The residence time for removing HCl is 4.5.
It was also confirmed that the time was as short as ~ 8.7 minutes.

【0042】[3] HClの除去装置の比較;表3
は、PE・PPにPVCを9.0wt%を混合し、常温
から段階的に昇温熱分解して最高温度320℃でHCl
除去を本発明装置で行つた場合と、既存の回分式装置で
等温下、320℃でHCl除去を行つた場合の除去割合
の結果を比較して示したものである。
[3] Comparison of HCl Removal Devices; Table 3
Is a mixture of PE and PP with 9.0 wt% of PVC, and is heated and decomposed in stages from room temperature to HCl at a maximum temperature of 320 ° C.
It is a comparison of the results of the removal ratios when the removal is performed by the device of the present invention and when the HCl removal is performed at 320 ° C. under the isothermal condition by the existing batch type device.

【0043】[0043]

【表3】 表3より、本発明装置によるHClの除去割合は、既存
の装置に比較して高い精度であり、HClの除去時間も
大幅に短縮されることを確認した。
[Table 3] From Table 3, it was confirmed that the removal rate of HCl by the apparatus of the present invention has higher accuracy than that of the existing apparatus, and the time for removing HCl is significantly shortened.

【0044】[4] 溶融固体生成物の減容化;表4
は、本発明装置でPE・PPにPVCを5.0wt%か
ら15.0wt%を混合し、常温から段階的に昇温さ
せ、最高温度を300℃と320℃とで熱分解して脱H
Cl処理と減容化した溶融固体生成物の見掛け密度を示
すものである。ここで、常温におけるPE・PPにPV
Cを5.0wt%から15wt%を混合した見掛けの密
度は約0.13kg/lである。
[4] Volume reduction of molten solid product; Table 4
In the apparatus of the present invention, PE / PP is mixed with PVC in an amount of 5.0 wt% to 15.0 wt%, the temperature is raised stepwise from room temperature, and the maximum temperature is thermally decomposed at 300 ° C. and 320 ° C. to remove H.
It shows the apparent density of the molten solid product subjected to Cl treatment and volume reduction. Here, PV is added to PE / PP at room temperature.
The apparent density of C mixed with 5.0 wt% to 15 wt% is about 0.13 kg / l.

【0045】[0045]

【表4】 表4より、300℃と320℃で処理して得た溶融固体
生成物の見掛けの密度は、0.76〜0.78kg/lと
なり、常温での見掛けの密度に比べて約1/6に減容化
することが明らかとなつた。
[Table 4] From Table 4, the apparent density of the molten solid product obtained by treating at 300 ° C. and 320 ° C. is 0.76 to 0.78 kg / l, which is about 1/6 of the apparent density at room temperature. It became clear that the volume would be reduced.

【0046】[5] ガス生成物中のHClの分析結
果;本発明装置を用いて、PE・PPにPVCを5.0
wt%から15.0wt%を混合し、常温から段階的に
昇温させ、最高温度を320℃で熱分解して生成したガ
ス成分中のHClの分析結果を表5に示した。
[5] Analytical result of HCl in gas product
Result: Using the device of the present invention, PVC was added to PE / PP at 5.0.
Table 5 shows the results of analysis of HCl in the gas components produced by mixing 1 wt% to 15.0 wt% of the mixture, gradually raising the temperature from room temperature, and thermally decomposing at a maximum temperature of 320 ° C.

【0047】[0047]

【表5】 表5より、生成したガス成分中のHCl濃度は、98.
6Vol%以上の高濃度であり、再利用が可能であるこ
とが分つた。
[Table 5] From Table 5, the HCl concentration in the produced gas component is 98.
It was found that the concentration was as high as 6 Vol% or more, and that it could be reused.

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

【図1】本発明の方法により、混合プラスチツク廃棄物
処理を行うために適した装置の一例の正面の概略図であ
る。
1 is a schematic front view of an example of an apparatus suitable for performing mixed plastic waste treatment according to the method of the present invention.

【図2】図1の平面の概略図である。FIG. 2 is a schematic view of the plane of FIG.

【図3】図1の右側面の概略図である。FIG. 3 is a schematic view of the right side surface of FIG.

【符号の説明】[Explanation of symbols]

1 熱分解反応装置 2 加熱ヒーター 3 温度調節器 4 反応筒 5−1 熱電対 5−2 熱電対 5−3 熱電対 6 ホツパー 7 異方向回転式二軸スクリユー 8 電機モーター 9 反応室 10 調整バルブ 11 ガス吸入管 12 融解固体物流出管 13 HCl回収器 14 吸引ポンプ 15 吸収塔 16 噴霧管 17 充填物 18 抜き出し管 19 吸着塔 1 Pyrolysis Reactor 2 Heater 3 Temperature Controller 4 Reaction Tube 5-1 Thermocouple 5-2 Thermocouple 5-3 Thermocouple 6 Hopper 7 Counter-rotating Biaxial Screw 8 Electric Motor 9 Reaction Chamber 10 Control Valve 11 Gas suction pipe 12 Molten solids outflow pipe 13 HCl recovery device 14 Suction pump 15 Absorption tower 16 Spray pipe 17 Packing material 18 Extraction pipe 19 Adsorption tower

───────────────────────────────────────────────────── フロントページの続き (72)発明者 鈴木 智 北海道札幌市豊平区月寒東2条17丁目2番 1号工業技術院北海道工業開発試験所内 (72)発明者 中谷 裕之 姫路市新在家中ノ町1−21 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Satoshi Suzuki Sat, Hokkaido, Toyohira-ku, Hokkaido 2-17-17 Tsukikanto, Industrial Technology Institute, Hokkaido Industrial Development Laboratory (72) Inventor Hiroyuki Nakatani New Home Nakanomachi, Himeji City 1-21

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 混合プラスチツク廃棄物を粉砕してなる
試料を、常温から330℃の範囲でしかも最高到達温度
が290〜330℃となるように段階的に昇温熱分解
し、しかる後ガス生成物と融解固体物に分離することを
特徴とする塩素が実質的に除去され且つ減容化された混
合プラスチツク廃棄物処理物を得るための処理方法。
1. A sample obtained by pulverizing mixed plastic waste is pyrolyzed in a temperature range from room temperature to 330 ° C. so that the maximum temperature reaches 290 to 330 ° C., and then gas products are obtained. And a molten solid, which is a treatment method for obtaining a mixed plastics waste treated product in which chlorine is substantially removed and the volume is reduced.
【請求項2】 混合プラスチツク廃棄物を粉砕してなる
試料を脱水した後昇温熱分解する請求項1記載の処理方
法。
2. The treatment method according to claim 1, wherein a sample obtained by pulverizing the mixed plastic waste is dehydrated and then thermally decomposed at elevated temperature.
【請求項3】 a) 混合プラスチツク廃棄物を粉砕し
てなる試料を段階的に昇温熱分解を行うための外部加熱
を有する熱分解反応装置、 b) 前記熱分解反応装置内に設置された反応筒に試料
を供給するためのホツパー、 c) 前記熱分解反応装置の反応筒内に試料を挿入する
異方向回転式二軸スクリユー、 d) 前記熱分解反応装置の反応筒出口側に加熱溶融し
た生成物を均一に混合する空間部分の反応室と流出圧力
を調整する調整バルブ e) 前記熱分解反応装置の反応筒出口の調整バルブか
ら流出するガス生成物と融解固体物とを分離するための
分離器及び f) ガス生成物から塩化水素(HCl)を回収するた
め回収器よりなる混合プラスチツク廃棄物の処理装置。
3. A pyrolysis reactor having external heating for stepwise thermal pyrolysis of a sample obtained by pulverizing mixed plastic waste, b) a reaction installed in the pyrolysis reactor. A hopper for supplying the sample to the cylinder, c) A bi-directional rotating biaxial screw for inserting the sample into the reaction tube of the thermal decomposition reaction apparatus, d) A heating tube melted on the outlet side of the reaction tube of the thermal decomposition reaction apparatus A reaction chamber in the space where the products are uniformly mixed and a regulating valve for regulating the outflow pressure e) for separating the gas product and the molten solid substance flowing out from the regulating valve at the outlet of the reaction tube of the thermal decomposition reactor Separator and f) Equipment for processing mixed plastic waste consisting of a collector for recovering hydrogen chloride (HCl) from gas products.
JP29770891A 1991-10-18 1991-10-18 Method and apparatus for treating mixed plastic waste Expired - Lifetime JP2648412B2 (en)

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JP29770891A JP2648412B2 (en) 1991-10-18 1991-10-18 Method and apparatus for treating mixed plastic waste

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WO1995015244A1 (en) * 1993-11-26 1995-06-08 Reinhard Fischer Process and apparatus for recycling waste polymers
EP0699735A1 (en) * 1994-08-31 1996-03-06 LINDE-KCA-Dresden GmbH Process for combined working up of PVC and other chlorinated hydrocarbons
JPH0971784A (en) * 1995-09-07 1997-03-18 Mitsui Petrochem Ind Ltd Method for converting waste plastic into oil
WO1998051459A1 (en) * 1997-05-09 1998-11-19 Nkk Corporation Method of and apparatus for granulating waste plastic in waste plastic recycling equipment
EP0890629A1 (en) * 1997-07-10 1999-01-13 Sinanen Co., Ltd. Pyrolytic Reactor for Waste Plastic
JP2000265173A (en) * 1999-03-11 2000-09-26 Ishikawajima Harima Heavy Ind Co Ltd Method and system for dry distillation-type cracking
JP2001101940A (en) * 1999-10-01 2001-04-13 Japan Steel Works Ltd:The Method and apparatus for recycling covering material of electric cable
US6346220B1 (en) 1997-01-31 2002-02-12 Kabushiki Kaisha Toshiba Waste plastic dechlorination apparatus
JP2003105124A (en) * 2001-09-28 2003-04-09 Toshiba Corp Waste plastic dechlorination control unit
JP2007190706A (en) * 2006-01-17 2007-08-02 Nippon Steel Corp Vacuum pump water-sealing treatment method for volume reducing molding machine of waste plastic and treatment equipment
KR100753250B1 (en) * 2006-08-23 2007-08-30 서울시립대학교 산학협력단 Screw pyrolysis reactor
CN102671913A (en) * 2012-05-04 2012-09-19 张文知 Comprehensive utilization method for waste aluminum-plastic paper composite packing material
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WO1995015244A1 (en) * 1993-11-26 1995-06-08 Reinhard Fischer Process and apparatus for recycling waste polymers
EP0699735A1 (en) * 1994-08-31 1996-03-06 LINDE-KCA-Dresden GmbH Process for combined working up of PVC and other chlorinated hydrocarbons
JPH0971784A (en) * 1995-09-07 1997-03-18 Mitsui Petrochem Ind Ltd Method for converting waste plastic into oil
US6346220B1 (en) 1997-01-31 2002-02-12 Kabushiki Kaisha Toshiba Waste plastic dechlorination apparatus
WO1998051459A1 (en) * 1997-05-09 1998-11-19 Nkk Corporation Method of and apparatus for granulating waste plastic in waste plastic recycling equipment
EP0890629A1 (en) * 1997-07-10 1999-01-13 Sinanen Co., Ltd. Pyrolytic Reactor for Waste Plastic
KR100700190B1 (en) * 1997-07-10 2007-07-09 시나넨 가부시키가이샤 Pyrolysis reaction device for waste plastic
JP2000265173A (en) * 1999-03-11 2000-09-26 Ishikawajima Harima Heavy Ind Co Ltd Method and system for dry distillation-type cracking
JP4650963B2 (en) * 1999-10-01 2011-03-16 株式会社日本製鋼所 Electric wire coating material recycling method and recycling apparatus
JP2001101940A (en) * 1999-10-01 2001-04-13 Japan Steel Works Ltd:The Method and apparatus for recycling covering material of electric cable
JP2003105124A (en) * 2001-09-28 2003-04-09 Toshiba Corp Waste plastic dechlorination control unit
JP4542510B2 (en) * 2006-01-17 2010-09-15 新日本製鐵株式会社 Vacuum pump seal water treatment method and treatment equipment for waste plastic volume reduction molding machine
JP2007190706A (en) * 2006-01-17 2007-08-02 Nippon Steel Corp Vacuum pump water-sealing treatment method for volume reducing molding machine of waste plastic and treatment equipment
KR100753250B1 (en) * 2006-08-23 2007-08-30 서울시립대학교 산학협력단 Screw pyrolysis reactor
CN102671913A (en) * 2012-05-04 2012-09-19 张文知 Comprehensive utilization method for waste aluminum-plastic paper composite packing material
GB2502126A (en) * 2012-05-17 2013-11-20 Oil From Waste Ltd Thermal decomposition of waste plastic
WO2013171510A1 (en) * 2012-05-17 2013-11-21 Oil From Waste Limited Processing waste polymeric material

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