[go: up one dir, main page]

JPH1190387A - Waste plastic dechlorination method and dechlorination equipment - Google Patents

Waste plastic dechlorination method and dechlorination equipment

Info

Publication number
JPH1190387A
JPH1190387A JP9259132A JP25913297A JPH1190387A JP H1190387 A JPH1190387 A JP H1190387A JP 9259132 A JP9259132 A JP 9259132A JP 25913297 A JP25913297 A JP 25913297A JP H1190387 A JPH1190387 A JP H1190387A
Authority
JP
Japan
Prior art keywords
reaction vessel
waste
waste plastics
waste plastic
plastic
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP9259132A
Other languages
Japanese (ja)
Inventor
Makoto Sugiyama
誠 杉山
Hironori Inokawa
弘徳 猪川
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.)
Kubota Corp
Original Assignee
Kubota 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 Kubota Corp filed Critical Kubota Corp
Priority to JP9259132A priority Critical patent/JPH1190387A/en
Publication of JPH1190387A publication Critical patent/JPH1190387A/en
Pending 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

Landscapes

  • Fire-Extinguishing Compositions (AREA)
  • Processing Of Solid Wastes (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Abstract

PROBLEM TO BE SOLVED: To continuously and stably obtain molten plastics which are low in chlorine concn. and are low in the contents of foreign matter and residues as well by maintaining the waste plastics while agitating and mixing the waste plastics under a specific pressure, temp. and time in a reducing atmosphere. SOLUTION: The waste plastics P1 contg. polyvinyl chloride, etc., are pulverized and are fed into a hopper 8. The waste plastics P1 are dropped into a screw feeder 9, are sent toward an outflow end. and are introduced to a waste plastic feeding port 2, from which the waste plastics are dropped into a reaction vessel 1. The dropped waste plastics P1 are heated to about 200 to 320 deg.C by hot medium oil 25 passed into a heat medium jacket 6 under the pressure below 1 kgf/cm<2> G controlled by a pressure control means 11 in a reduction atmosphere to which oxygen is not supplied. The waste plastics are held for a prescribed time of >=1 hour under agitating and mixing. As a result, the acidic gases, such as hydrogen chloride, formed by the pyrolysis of the PVC, etc., are removed and the gravity settled foreign matter and residues are easily discharged.

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、ポリ塩化ビニルを
含んだ廃プラスチックの脱塩素方法および脱塩素装置に
関する。
The present invention relates to a method and an apparatus for dechlorinating waste plastics containing polyvinyl chloride.

【0002】[0002]

【従来の技術】容器包装リサイクル法の制定により、廃
プラスチックの再利用が要求されている。現在提案され
ている再利用方法としては、高炉に吹き込んで還元剤と
して利用する方法、セメント等の原料として利用する方
法、油化等による燃料化などがある。
2. Description of the Related Art The enactment of the Containers and Packaging Recycling Law requires the reuse of waste plastics. Currently proposed recycling methods include a method in which the material is blown into a blast furnace to be used as a reducing agent, a method in which the material is used as a raw material for cement or the like, and a method in which oil is used as a fuel.

【0003】しかし、廃プラスチックにポリ塩化ビニル
が含まれていると、その塩素分が加熱工程で塩化水素化
し、反応装置の腐食や大気汚染を招いたり、塩素分を含
んだ製品が得られ、製品を利用する設備の腐食や有毒ガ
スの発生などを引き起こすため、種々の塩素対策が講じ
られている。
[0003] However, if polyvinyl chloride is contained in waste plastics, the chlorine content is converted into hydrogen chloride in the heating step, causing corrosion of the reactor and air pollution, and obtaining products containing chlorine content. Various measures against chlorine have been taken in order to cause corrosion of equipment using the product and generation of toxic gas.

【0004】たとえば、特開昭55−121875号に
記載の廃棄物処理方法および装置では、廃プラッスチッ
クまたは廃プラスチックを含有する廃棄物をアルカリ剤
とともに密閉容器に投入し、この容器を外部から加熱し
て廃棄物を溶融し、廃棄物の溶融に伴って発生する塩化
水素などの酸性ガスをアルカリ剤で中和するようにして
おり、これにより、酸性ガスによる装置の腐食や大気汚
染を防止し、溶融物の冷却によって得られる塊状物を建
設用ブロック等として再利用するようにしている。
[0004] For example, in the waste disposal method and apparatus described in Japanese Patent Application Laid-Open No. 55-121875, waste containing waste plastic or waste plastic is put into a closed container together with an alkali agent, and the container is heated from the outside. To melt the waste and neutralize acidic gas such as hydrogen chloride generated with the melting of the waste with an alkaline agent, thereby preventing corrosion of equipment and air pollution by the acidic gas, Agglomerates obtained by cooling the melt are reused as construction blocks and the like.

【0005】特開平6−65582号に記載の廃プラス
チックの脱塩素・分離装置では、廃プラスチックの燃料
化(固形燃料、油化、ガス化)の前処理として、廃プラ
スチックを加熱溶融しつつ槽内に導入し、槽内の溶融物
を外部からの加熱により300℃程度に保持して脱塩素
化を行い、生じた炭化物を槽外へ取り出すことにより、
脱塩素化され炭化物が除去された溶融プラスチックを得
るようにしている。
In the waste plastic dechlorination / separation apparatus described in Japanese Patent Application Laid-Open No. 6-65582, as a pretreatment for converting waste plastic into fuel (solid fuel, oil, gasification), the waste plastic is heated and melted. Into the tank, dechlorination is performed by holding the melt in the tank at about 300 ° C. by heating from the outside, and the resulting carbide is taken out of the tank.
It is intended to obtain a molten plastic which is dechlorinated and free of carbides.

【0006】特開平8−120285に記載の廃プラス
チックの熱分解反応装置では、廃プラスチック投入口よ
り反応筒内に投入した廃棄プラスチックを、戻り流路を
通って投入口近傍に戻った溶融プラスチックと混合する
ことで加熱溶融し、この溶融プラスチックを羽根によっ
て溶融プラスチック流出口に向かう方向に送り出し、そ
の際に外部加熱手段と内部加熱手段とで内外から加熱す
るとともに羽根で混練することにより、温度均一化を図
って熱分解反応を促進し、塩素濃度の低い溶融プラスチ
ックを得るようにしている。
In the waste plastic pyrolysis reaction apparatus described in Japanese Patent Application Laid-Open No. H8-120285, waste plastic introduced into a reaction tube from a waste plastic input port is mixed with molten plastic returned to the vicinity of the input port through a return flow path. The molten plastic is heated and melted by mixing, and the molten plastic is sent out in the direction toward the molten plastic outlet by the blades.At this time, the mixture is heated from the inside and outside by the external heating means and the internal heating means and kneaded by the blades, so that the temperature is uniform. To promote the thermal decomposition reaction to obtain molten plastic with low chlorine concentration.

【0007】[0007]

【発明が解決しようとする課題】しかしながら、上記し
た特開昭55−121875号に記載のものは、アルカ
リ剤を投入するため、製品の用途が上記したようなもの
に限定されてしまう。特開平6−65582号に記載の
ものは、外部からの加熱であるため急激な温度勾配が生
じ、発生した塩化水素に触れて低温腐食を起こす領域が
生じるだけでなく、異物や残渣を十分に抜き出せない。
特開平8−120285に記載のものは、反応筒内での
滞留時間が短いために発生した塩化水素などの酸性ガス
を十分に除去できず、装置腐食の問題が依然として残る
だけでなく、原料廃プラスチックに金属等の異物が混入
していると装置に損傷が生じ易く、そのような場合のメ
ンテナンスが容易でない等の欠点がある。
However, in the above-mentioned Japanese Patent Application Laid-Open No. 55-121875, the use of the product is limited to that described above because an alkali agent is added. Japanese Patent Application Laid-Open No. 6-65582 is a method of heating from the outside, so that a sharp temperature gradient is generated, and not only a region where low temperature corrosion is caused by touching the generated hydrogen chloride is generated, but also foreign substances and residues are sufficiently removed. I can't pull it out.
The method described in JP-A-8-120285 cannot sufficiently remove an acidic gas such as hydrogen chloride generated due to a short residence time in a reaction tube, not only leaving a problem of apparatus corrosion, but also a waste of raw materials. If foreign matter such as metal is mixed in the plastic, there is a drawback that the device is easily damaged and maintenance in such a case is not easy.

【0008】本発明は上記課題を解決するもので、塩素
濃度が低く、異物や残渣の含有量も少ない溶融プラスチ
ックを連続的安定的に造り出せるとともに、発生する酸
性ガスによる装置の腐食を防止できる廃プラスチックの
脱塩素方法および脱塩素装置を提供することを目的とす
るものである。
The present invention solves the above-mentioned problems, and can continuously and stably produce a molten plastic having a low chlorine concentration and a small content of foreign substances and residues, and can prevent corrosion of the apparatus due to generated acidic gas. It is an object of the present invention to provide a method and apparatus for dechlorinating waste plastic.

【0009】[0009]

【課題を解決するための手段】上記課題を解決するため
に、本発明は、ポリ塩化ビニルを含んだ廃プラスチック
の脱塩素方法であって、前記廃プラスチックを還元性雰
囲気中、1kgf/cm2 G未満の圧力下、攪拌混合し
ながら、約200〜320℃の温度に1時間以上維持す
ることにより、廃プラスチックを溶融させるとともに、
ポリ塩化ビニルを熱分解して、生成した塩化水素ガス等
のガスを排出し、脱塩素化された溶融プラスチックを取
り出すようにした廃プラスチックの脱塩素方法を提供す
るものである。
In order to solve the above-mentioned problems, the present invention is a method for dechlorinating waste plastics containing polyvinyl chloride, wherein the waste plastics are reduced to 1 kgf / cm 2 in a reducing atmosphere. By maintaining the temperature at about 200 to 320 ° C. for 1 hour or more while stirring and mixing under a pressure of less than G, the waste plastic is melted,
It is an object of the present invention to provide a method for dechlorinating waste plastics, in which a gas such as hydrogen chloride gas generated by thermally decomposing polyvinyl chloride is discharged and a dechlorinated molten plastic is taken out.

【0010】1kgf/cm2 G未満の低圧力下、20
0〜320℃の温度では、ポリ塩化ビニルと、高温領域
でポリエチレンテレフタレートが熱分解するが、その他
の廃プラスチック、すなわち、容器に利用されるポリス
チレン等のポリオレフィン系樹脂などのプラスチックは
熱分解しない。
Under a low pressure of less than 1 kgf / cm 2 G,
At a temperature of 0 to 320 ° C., polyvinyl chloride and polyethylene terephthalate are thermally decomposed in a high temperature range, but other waste plastics, that is, plastics such as polyolefin resin such as polystyrene used for containers are not thermally decomposed.

【0011】このため、廃プラスチックを上記条件下に
1時間以上維持すると、十分な熱分解反応時間が確保さ
れる状態において、ポリ塩化ビニルと、ポリエチレンテ
レフタレートが含まれている場合はポリエチレンテレフ
タレートが高温領域で熱分解し、その他の廃プラスチッ
クは熱分解することなく溶融し、熱分解によって生成し
た塩化水素ガスなどのガスは排出され、極めて塩素濃度
の低い溶融プラスチックが得られるとともに、反応装置
等の腐蝕は防止される。
For this reason, if the waste plastic is maintained for one hour or more under the above conditions, the polyvinyl terephthalate and the polyethylene terephthalate may be heated to a high temperature in a state where a sufficient pyrolysis reaction time is secured. Pyrolysis in the area, other waste plastics melt without pyrolysis, gases such as hydrogen chloride gas generated by the pyrolysis are discharged, and molten plastics with extremely low chlorine concentration can be obtained, as well as reaction equipment etc. Corrosion is prevented.

【0012】生成する塩化水素ガスなどの酸性ガスによ
る反応装置等の腐食をより効果的に回避するためには、
廃プラスチックを250℃以上に維持する。得られる溶
融プラスチックを油化に用いる場合は、油化装置内で昇
華物を生成するポリエチレンテレフタレートが十分に熱
分解されるように、廃プラスチックを約320℃程度に
維持する。
In order to more effectively prevent corrosion of a reaction device or the like due to generated acidic gas such as hydrogen chloride gas,
Maintain the waste plastic above 250 ° C. When the obtained molten plastic is used for oiling, the waste plastic is maintained at about 320 ° C. so that polyethylene terephthalate which generates sublimate is sufficiently thermally decomposed in the oiling apparatus.

【0013】本発明はまた、上記した廃プラスチックの
脱塩素方法を実施する脱塩素装置であって、上部に廃プ
ラスチック投入口とガス流出口とを形成し、コーン状を
なす下部に溶融プラスチック取出口と残渣抜出口とをこ
の順に上下に形成した密閉式の反応容器と、この反応容
器を外部から加熱する加熱手段と、反応容器の内側面近
傍を周方向に移動する攪拌羽根を有した攪拌手段と、前
記加熱手段を介して反応容器の内容物を所定温度に調節
する温度調節手段と、反応容器内のガス圧を所定圧力に
調節する圧力調節手段とを備えた廃プラスチックの脱塩
素装置を提供する。
The present invention is also a dechlorination apparatus for performing the above-described method for dechlorinating waste plastic, wherein a waste plastic inlet and a gas outlet are formed in the upper part, and a molten plastic collector is formed in the cone-shaped lower part. Stirring having a sealed reaction vessel in which an outlet and a residue discharge port are formed vertically in this order, a heating means for heating the reaction vessel from the outside, and a stirring blade moving circumferentially near the inner surface of the reaction vessel. Waste plastic dechlorination apparatus comprising: means, a temperature adjusting means for adjusting the contents of the reaction vessel to a predetermined temperature via the heating means, and a pressure adjusting means for adjusting the gas pressure in the reaction vessel to a predetermined pressure. I will provide a.

【0014】上記した構成によれば、廃プラスチック投
入口を通じて反応容器の内部に廃プラスチックを投入す
ると、投入された廃プラスチックは、容器の外部の加熱
手段によって間接的に加熱され、攪拌羽根によって周方
向に攪拌混合される状態において溶融する。
According to the above configuration, when the waste plastic is charged into the reaction vessel through the waste plastic charging port, the waste plastic is heated indirectly by the heating means outside the vessel and is rotated by the stirring blade. Melts in a state where it is stirred and mixed in the direction.

【0015】その際に、圧力調節手段によって反応容器
内のガス圧が所定圧力に調節されるとともに、温度調節
手段により加熱手段を介して反応容器の内容物が所定温
度に調節されるため、所定圧力、所定温度の下で熱分解
する樹脂のみが熱分解し、生成したガスは攪拌混合に伴
ってガス流出口より流出する。
At this time, the gas pressure in the reaction vessel is adjusted to a predetermined pressure by the pressure adjusting means, and the content of the reaction vessel is adjusted to the predetermined temperature via the heating means by the temperature adjusting means. Only the resin that thermally decomposes under a predetermined pressure and temperature is thermally decomposed, and the generated gas flows out from the gas outlet with stirring and mixing.

【0016】熱分解することなく溶融した廃プラスチッ
クは溶融プラスチックとして下部の溶融プラスチック取
出口から取り出され、廃プラスチック中に混入していた
異物や廃プラスチックの熱分解で生じた残渣は、攪拌羽
根によって掻き上げられることなく沈降し、下部内側面
の傾斜に沿って移動して底部に集まり、残渣抜出口より
適宜抜き出される。
The waste plastic that has been melted without being thermally decomposed is taken out of the lower molten plastic outlet as molten plastic, and foreign substances mixed in the waste plastic and residues generated by thermal decomposition of the waste plastic are removed by a stirring blade. It settles without being scraped up, moves along the slope of the lower inner surface, gathers at the bottom, and is appropriately extracted from the residue extraction outlet.

【0017】攪拌羽根に、反応容器の内側面に摺接して
付着物を掻き取る掻取板を装着した構成としてもよく、
この場合、廃プラスチックの熱分解によって発生し、反
応容器の内側面に付着したカーボン残渣も効果的に取り
除かれる。
[0017] The stirring blade may be provided with a scraping plate for slidingly contacting the inner surface of the reaction vessel to scrape off the deposits.
In this case, carbon residues generated by thermal decomposition of the waste plastic and attached to the inner surface of the reaction vessel are also effectively removed.

【0018】[0018]

【発明の実施の形態】以下、本発明の実施の形態を図面
を参照しながら説明する。図1において、本発明の一実
施形態における廃プラスチックの脱塩素装置は、上部が
筒状をなし下部がコーン状をなす密閉式の反応容器1を
備えており、この反応容器1は、天部に廃プラスチック
投入口2とガス流出口3とを配し、下部に溶融プラスチ
ック取出口4と残渣抜出口5とをこの順に上下に配し、
外周面をほぼ全体にわたって覆う熱媒ジャケット6と、
内容物を攪拌混合する攪拌装置7とを有している。
Embodiments of the present invention will be described below with reference to the drawings. In FIG. 1, a waste plastic dechlorination apparatus according to an embodiment of the present invention includes a closed reaction vessel 1 having an upper part having a cylindrical shape and a lower part having a cone shape. A waste plastic inlet 2 and a gas outlet 3, and a lower part of a molten plastic outlet 4 and a residue outlet 5 at a lower part in this order.
A heat medium jacket 6 covering substantially the entire outer peripheral surface;
And a stirrer 7 for stirring and mixing the contents.

【0019】廃プラスチック投入口2の上方には、一端
上部にホッパ8を備え水平に配されたスクリューフィー
ダー9の流出端が位置している。ガス流出口3には、防
食処理したガス抜出管10が接続しており、このガス抜
出管10に、反応容器1内のガス圧を所定圧力に調節す
るための圧力調節手段11と、冷却手段(図示せず)を
有した昇華物分離装置12と、苛性ソーダ水溶液(図示
せず)などの酸性ガス中和手段を有した中和装置13と
が介装されている。上記圧力調節手段11はたとえば、
反応容器1の内部に連通したこのガス抜出管10の内部
のガス圧を検知する圧力計11aと、検知されたガス圧
と維持すべき反応容器内の所定圧力とを比較し、両者の
圧力差に応じた量のガスを通過させるように流量弁11
bを制御する制御装置11cとで構成される。
Above the waste plastic inlet 2, the outflow end of a horizontally arranged screw feeder 9 having a hopper 8 at one end is located. The gas outlet 3 is connected to a gas extraction pipe 10 which has been subjected to anticorrosion treatment. The gas extraction pipe 10 has a pressure adjusting means 11 for adjusting the gas pressure in the reaction vessel 1 to a predetermined pressure. A sublimate separation device 12 having a cooling means (not shown) and a neutralization device 13 having an acid gas neutralizing means such as an aqueous caustic soda solution (not shown) are interposed. The pressure adjusting means 11 is, for example,
The pressure gauge 11a for detecting the gas pressure inside the gas extraction pipe 10 communicating with the inside of the reaction vessel 1 is compared with the detected gas pressure and a predetermined pressure in the reaction vessel to be maintained. A flow valve 11 is provided so as to pass an amount of gas corresponding to the difference.
and a control device 11c for controlling b.

【0020】溶融プラスチック取出口4の側方には、一
端下部に排出口14を備え水平方向に配された溶融プラ
スチック取出装置15の流入端が位置し、残渣抜出口5
の下方には、一端下部に排出口16を備え水平方向に配
された残渣取出装置17の流入端が位置している。各取
出装置15,17は二重管構造を有していて、内管の内
部に案内手段18,19が配され、内管と外管との間に
冷却水流路20,21が形成されている。
At the side of the molten plastic outlet 4, the inflow end of a horizontally disposed molten plastic extracting device 15 having an outlet 14 at one lower end is located.
Below, is located an inflow end of a residue removing device 17 which is provided with a discharge port 16 at one end lower portion and is disposed in a horizontal direction. Each of the extraction devices 15 and 17 has a double pipe structure, in which guide means 18 and 19 are disposed inside the inner pipe, and cooling water flow paths 20 and 21 are formed between the inner pipe and the outer pipe. I have.

【0021】熱媒ジャケット6の外側には、熱媒ジャケ
ット6の下部に形成された流入口22と、上部に形成さ
れた流出口23とを連通する熱媒循環路24が設けら
れ、その途中に、加熱流体としての熱媒油25を所定温
度に加熱する加熱装置26が設けられている。
Outside the heat medium jacket 6, there is provided a heat medium circulation path 24 which connects an inflow port 22 formed at a lower part of the heat medium jacket 6 and an outflow port 23 formed at an upper part thereof. Is provided with a heating device 26 for heating the heating medium oil 25 as a heating fluid to a predetermined temperature.

【0022】攪拌装置7は、反応容器1の上方のモータ
ー27に駆動軸28を介して接続する上下方向のシャフ
ト29と、反応容器1の内側面に沿うくの字状に形成さ
れ、反応容器1の径方向に配された支持部材30,31
を介してシャフト29に固着された複数枚の攪拌羽根3
2と、各攪拌羽根32に固着して反応容器1の内側面に
摺接状態に設けられた掻取板33とを有している。
The stirrer 7 has a vertical shaft 29 connected to a motor 27 above the reaction vessel 1 via a drive shaft 28, and a V-shape along the inner surface of the reaction vessel 1. 1 support members 30, 31 arranged in the radial direction
Blades 3 fixed to shaft 29 through
2 and a scraping plate 33 fixed to each stirring blade 32 and slidably provided on the inner surface of the reaction vessel 1.

【0023】上記した構成における作用を説明する。ポ
リ塩化ビニルやポリエチレンテレフタレートを含んだ廃
プラスチックP1を粉砕してホッパ8に投入すると、ホ
ッパ8内の廃プラスチックP1はスクリューフィーダー
9の内部に落下し、流出端へ向けて送られ、廃プラスチ
ック投入口2へ導かれて反応容器1の内部へ落下する。
The operation of the above configuration will be described. When the waste plastic P1 containing polyvinyl chloride or polyethylene terephthalate is pulverized and put into the hopper 8, the waste plastic P1 in the hopper 8 falls into the screw feeder 9, is sent toward the outflow end, and is put into the waste plastic. The liquid is guided to the port 2 and falls into the reaction vessel 1.

【0024】反応容器1内に落下した廃プラスチックP
1は、酸素供給されない還元性雰囲気中、圧力調節手段
11によって調節される1kgf/cm2 G未満の圧力
下に、熱媒ジャケット6の内部に流通される熱媒油25
によって約320℃に加熱され、攪拌羽根32によって
周方向に攪拌混合されながら、一時間以上の所定時間保
持される。
Waste plastic P dropped into reaction vessel 1
1 is a heating medium oil 25 flowing through the inside of the heating medium jacket 6 under a pressure of less than 1 kgf / cm 2 G adjusted by the pressure adjusting means 11 in a reducing atmosphere to which oxygen is not supplied.
To about 320 ° C., and is held for a predetermined time of one hour or more while being stirred and mixed in the circumferential direction by the stirring blade 32.

【0025】これにより、1kgf/cm2 G未満の低
圧力、約320℃の温度でポリ塩化ビニルとポリエチレ
ンテレフタレートが熱分解し、熱分解によって生成した
塩化水素などの酸性ガスやポリエチレンテレフタレート
の分解物(テレフタル酸)などのガスがガス流出口3を
通じて流出していき、その他の廃プラスチックP1は熱
分解することなく溶融する。
As a result, polyvinyl chloride and polyethylene terephthalate are thermally decomposed at a low pressure of less than 1 kgf / cm 2 G and at a temperature of about 320 ° C., and an acid gas such as hydrogen chloride generated by the pyrolysis or a decomposition product of polyethylene terephthalate. A gas such as (terephthalic acid) flows out through the gas outlet 3, and the other waste plastic P1 is melted without being thermally decomposed.

【0026】このようにして脱塩素されポリエチレンテ
レフタレート除去された溶融プラスチックP2は、所定
時間後に溶融プラスチック取出口4を通じて取り出さ
れ、溶融プラスチック取出装置15の流入端に導入さ
れ、冷却水流路20を流れる冷却水wによって冷却され
つつ、案内手段18によって排出口14に向けて案内さ
れ、その間に固化して、固形プラスチックP3として排
出口14から搬出装置(図示せず)の上へ排出される。
The molten plastic P2 thus dechlorinated and from which polyethylene terephthalate has been removed is taken out through the molten plastic take-out port 4 after a predetermined time, introduced into the inflow end of the molten plastic take-out device 15, and flows through the cooling water flow path 20. While being cooled by the cooling water w, it is guided toward the discharge port 14 by the guide means 18, solidified during that time, and discharged as solid plastic P3 from the discharge port 14 onto a carry-out device (not shown).

【0027】ガス流出口3より流出したガスはガス抜出
管10を通じて反応容器1の外部へと導かれ、その管路
途中で、昇華物分離装置12において冷却されることに
よりポリエチレンテレフタレートの分解物が昇華して分
離され、中和装置13において塩化水素などの酸性ガス
が苛性ソーダ水溶液で中和され除去される。
The gas flowing out from the gas outlet 3 is guided to the outside of the reaction vessel 1 through a gas extraction pipe 10, and is cooled in a sublimate separation device 12 in the middle of the pipe, thereby decomposing polyethylene terephthalate. Is sublimated and separated, and an acid gas such as hydrogen chloride is neutralized and removed by a caustic soda aqueous solution in the neutralization device 13.

【0028】廃プラスチックP1中に混入していたガラ
ス、金属、カルシウム化合物等の異物は、攪拌羽根32
に掻き上げられることなく沈降し、熱分解により生成し
て内側面に付着したカーボン残渣は掻取板33によって
掻き取られ、ともに傾斜面に沿って底部へ移動する。そ
して、残渣抜出口5より残渣Rとして適宜抜き出され、
残渣取出装置17の流入端に導かれ、冷却水流路21を
流れる冷却水wによって冷却されつつ、案内手段19に
よって排出口16に向けて案内され、排出口16から搬
出装置(図示せず)の上へ排出される。
Foreign substances such as glass, metal, calcium compound and the like mixed in the waste plastic P1 are removed by the stirring blade 32.
The carbon residue generated by thermal decomposition and attached to the inner surface is scraped off by the scraping plate 33 and moved to the bottom along the inclined surface. Then, it is appropriately extracted as a residue R from the residue discharge port 5, and
It is guided to the discharge port 16 by the guide means 19 while being guided by the cooling water w flowing through the cooling water flow path 21 while being guided to the inflow end of the residue removing device 17, and the discharge device (not shown) is discharged from the discharge port 16. Discharged up.

【0029】なお、上記においては、得られる溶融プラ
スチックP2(固形プラスチックP3)を油化するもの
として、廃プラスチックP1の温度を320℃程度まで
上げ、ポリ塩化ビニルとともにポリエチレンテレフタレ
ートを熱分解するようにして、油化装置内におけるコー
キングや昇華物の生成を防止できるようにしたが、油化
しない場合には、ポリエチレンテレフタレートを熱分解
する必要はないので、ポリ塩化ビニルを選択的に熱分解
できる温度であって、生成する酸性ガスによる反応容器
1等の腐食を避けられる200℃以上、望ましくは25
0℃以上、約290℃以下に保てばよい。
In the above, assuming that the obtained molten plastic P2 (solid plastic P3) is converted to oil, the temperature of the waste plastic P1 is raised to about 320 ° C. so that polyethylene terephthalate is thermally decomposed together with polyvinyl chloride. To prevent coking and the formation of sublimates in the oiling device, but when oiling is not used, there is no need to thermally decompose polyethylene terephthalate. 200 ° C. or higher, preferably 25 ° C. or more, in which corrosion of the reaction vessel 1 and the like due to generated acidic gas can be avoided.
The temperature may be maintained at 0 ° C. or higher and about 290 ° C. or lower.

【0030】また上記においては回分式の運転方法を説
明したが、廃プラスチックを連続投入し、溶融プラスチ
ックを連続取り出しする連続式の運転をしてもよく、こ
の場合、残留塩素の点では回分式より幾分劣るものの、
塩素濃度が十分に低い製品を連続的かつ安定的に得るこ
とができる。
Although the batch type operation method has been described above, a continuous type operation in which waste plastics are continuously charged and molten plastics are continuously taken out may be employed. Although somewhat inferior,
A product having a sufficiently low chlorine concentration can be obtained continuously and stably.

【0031】[0031]

【発明の効果】以上のように、本発明の脱塩素方法およ
び脱塩素装置によれば、廃プラスチックをポリオレフィ
ン系樹脂などの熱分解温度より低い所定温度に1時間以
上保持することにより、十分な反応時間を確保する状態
において、廃プラスチック中に含まれるポリ塩化ビニル
を選択的にかつ完全に熱分解し、生成した塩化水素など
の酸性ガスを除去し、比重沈降する異物や残渣を容易に
排出することができ、塩素濃度が低く、異物や残渣の含
有量が少ない製品が得られる。また前記所定温度では発
生する酸性ガスによる腐食は起こらないので、反応容器
や攪拌装置などに特殊材料を使用する必要はない。
As described above, according to the dechlorination method and the dechlorination apparatus of the present invention, by maintaining the waste plastic at a predetermined temperature lower than the thermal decomposition temperature of the polyolefin resin or the like for one hour or more, In a state where the reaction time is secured, the polyvinyl chloride contained in the waste plastic is selectively and completely thermally decomposed, the generated acidic gas such as hydrogen chloride is removed, and foreign substances and residues that settle down with specific gravity are easily discharged. Thus, a product having a low chlorine concentration and a low content of foreign substances and residues can be obtained. At the above-mentioned predetermined temperature, corrosion due to the generated acidic gas does not occur, so that it is not necessary to use a special material for the reaction vessel, the stirrer and the like.

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

【図1】本発明の一実施形態における廃プラスチックの
脱塩素装置の概略全体構成を示した説明図である。
FIG. 1 is an explanatory diagram showing a schematic overall configuration of a waste plastic dechlorination apparatus according to an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 反応容器 2 廃プラスチック投入口 3 ガス流出口 4 溶融プラスチック取出口 5 残渣抜出口 6 熱媒ジャケット 11 圧力調節手段 25 熱媒油 26 加熱装置 32 攪拌羽根 33 掻取板 P1 廃プラスチック P2 溶融プラスチック P3 固形プラスチック R 残渣 Reference Signs List 1 reaction vessel 2 waste plastic inlet 3 gas outlet 4 molten plastic outlet 5 residue discharge outlet 6 heating medium jacket 11 pressure control means 25 heating medium oil 26 heating device 32 stirring blade 33 scraping plate P1 waste plastic P2 molten plastic P3 Solid plastic R residue

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 ポリ塩化ビニルを含んだ廃プラスチック
の脱塩素方法であって、前記廃プラスチックを還元性雰
囲気中、1kgf/cm2 G未満の圧力下、攪拌混合し
ながら、約200〜320℃の温度に1時間以上維持す
ることにより、廃プラスチックを溶融させるとともに、
ポリ塩化ビニルを熱分解して、生成した塩化水素ガス等
のガスを排出し、脱塩素化された溶融プラスチックを取
り出すことを特徴とする廃プラスチックの脱塩素方法。
1. A method for dechlorinating waste plastics containing polyvinyl chloride, wherein said waste plastics are stirred at about 200-320 ° C. in a reducing atmosphere under a pressure of less than 1 kgf / cm 2 G. By maintaining the temperature of at least 1 hour, the waste plastic is melted,
A method for dechlorinating waste plastics, which comprises decomposing polyvinyl chloride by pyrolysis, discharging gas such as hydrogen chloride gas produced, and taking out dechlorinated molten plastic.
【請求項2】 廃プラスチックを250℃以上に維持す
ることを特徴とする請求項1記載の廃プラスチックの脱
塩素方法。
2. The method for dechlorinating waste plastic according to claim 1, wherein the waste plastic is maintained at 250 ° C. or higher.
【請求項3】 廃プラスチックを約320℃に維持する
ことを特徴とする請求項1記載の廃プラスチックの脱塩
素方法。
3. The method of claim 1 wherein the waste plastic is maintained at about 320 ° C.
【請求項4】 上部に廃プラスチック投入口とガス流出
口とを形成し、コーン状をなす下部に溶融プラスチック
取出口と残渣抜出口とをこの順に上下に形成した密閉式
の反応容器と、この反応容器を外部から加熱する加熱手
段と、反応容器の内側面近傍を周方向に移動する攪拌羽
根を有した攪拌手段と、前記加熱手段を介して反応容器
の内容物を所定温度に調節する温度調節手段と、反応容
器内のガス圧を所定圧力に調節する圧力調節手段とを備
えたことを特徴とする廃プラスチックの脱塩素装置。
4. A hermetically sealed reaction vessel having a waste plastic inlet and a gas outlet formed in the upper part, a molten plastic outlet and a residue outlet formed in the lower part in a cone shape in this order. Heating means for heating the reaction vessel from the outside, stirring means having stirring blades moving in the circumferential direction near the inner surface of the reaction vessel, and a temperature for adjusting the contents of the reaction vessel to a predetermined temperature via the heating means. An apparatus for dechlorinating waste plastics, comprising: an adjusting means; and a pressure adjusting means for adjusting a gas pressure in a reaction vessel to a predetermined pressure.
【請求項5】 攪拌羽根に、反応容器の内側面に摺接し
て付着物を掻き取る掻取板を装着したことを特徴とする
請求項4記載の廃プラスチックの脱塩素装置。
5. The apparatus for dechlorinating waste plastic according to claim 4, wherein a scraping plate for slidingly contacting the inner surface of the reaction vessel and scraping off the adhered substance is mounted on the stirring blade.
JP9259132A 1997-09-25 1997-09-25 Waste plastic dechlorination method and dechlorination equipment Pending JPH1190387A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9259132A JPH1190387A (en) 1997-09-25 1997-09-25 Waste plastic dechlorination method and dechlorination equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9259132A JPH1190387A (en) 1997-09-25 1997-09-25 Waste plastic dechlorination method and dechlorination equipment

Publications (1)

Publication Number Publication Date
JPH1190387A true JPH1190387A (en) 1999-04-06

Family

ID=17329773

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9259132A Pending JPH1190387A (en) 1997-09-25 1997-09-25 Waste plastic dechlorination method and dechlorination equipment

Country Status (1)

Country Link
JP (1) JPH1190387A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2007115443A1 (en) * 2006-04-07 2007-10-18 Bin Niu A continuous pyrolyzing process for waste rubber or plastics
JP2008106127A (en) * 2006-10-25 2008-05-08 Ube Ind Ltd Solid fuel and method for producing cement clinker using the same
KR100829212B1 (en) 2007-01-18 2008-05-14 정문현 Waste Vinyl Recovery Device
CN109705888A (en) * 2019-01-16 2019-05-03 武汉博立达农业科技发展有限公司 Regenerative rotary bed
JP2020157667A (en) * 2019-03-27 2020-10-01 凸版印刷株式会社 Non-combustible sheet recycling method and non-combustible sheet recycling device
CN115261053A (en) * 2022-06-29 2022-11-01 光大环境科技(中国)有限公司 Continuous sample injection waste plastic catalytic cracking oil production device and method
WO2023223932A1 (en) * 2022-05-16 2023-11-23 環境エネルギー株式会社 Continuous organic matter pyrolysis device and continuous organic matter pyrolysis method
WO2024139623A1 (en) * 2022-12-29 2024-07-04 中国石油天然气股份有限公司 Waste plastic treatment method and device

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5170281U (en) * 1974-11-27 1976-06-03
JPH0782569A (en) * 1993-09-13 1995-03-28 Toshiba Corp Method and apparatus for thermal liquefaction
JPH07286062A (en) * 1994-04-19 1995-10-31 Mitsubishi Heavy Ind Ltd Method for treating chlorine-containing plastic waste
JPH0913044A (en) * 1995-07-01 1997-01-14 Nippon Furnace Kogyo Kaisha Ltd Decomposition vessel of waste plastic liquefaction apparatus
JPH0913043A (en) * 1995-07-01 1997-01-14 Nippon Furnace Kogyo Kaisha Ltd Decomposition vessel of waste plastic liquefaction apparatus
JPH09249766A (en) * 1996-03-15 1997-09-22 Toshiba Corp Process for treating plastic waste

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5170281U (en) * 1974-11-27 1976-06-03
JPH0782569A (en) * 1993-09-13 1995-03-28 Toshiba Corp Method and apparatus for thermal liquefaction
JPH07286062A (en) * 1994-04-19 1995-10-31 Mitsubishi Heavy Ind Ltd Method for treating chlorine-containing plastic waste
JPH0913044A (en) * 1995-07-01 1997-01-14 Nippon Furnace Kogyo Kaisha Ltd Decomposition vessel of waste plastic liquefaction apparatus
JPH0913043A (en) * 1995-07-01 1997-01-14 Nippon Furnace Kogyo Kaisha Ltd Decomposition vessel of waste plastic liquefaction apparatus
JPH09249766A (en) * 1996-03-15 1997-09-22 Toshiba Corp Process for treating plastic waste

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2007115443A1 (en) * 2006-04-07 2007-10-18 Bin Niu A continuous pyrolyzing process for waste rubber or plastics
US8168839B2 (en) 2006-04-07 2012-05-01 Bin Niu Continuously cracking technology of waste rubber or plastics and its equipment
JP2008106127A (en) * 2006-10-25 2008-05-08 Ube Ind Ltd Solid fuel and method for producing cement clinker using the same
KR100829212B1 (en) 2007-01-18 2008-05-14 정문현 Waste Vinyl Recovery Device
CN109705888A (en) * 2019-01-16 2019-05-03 武汉博立达农业科技发展有限公司 Regenerative rotary bed
JP2020157667A (en) * 2019-03-27 2020-10-01 凸版印刷株式会社 Non-combustible sheet recycling method and non-combustible sheet recycling device
WO2023223932A1 (en) * 2022-05-16 2023-11-23 環境エネルギー株式会社 Continuous organic matter pyrolysis device and continuous organic matter pyrolysis method
JP2023169001A (en) * 2022-05-16 2023-11-29 環境エネルギー株式会社 Continuous organic matter pyrolysis method
CN115261053A (en) * 2022-06-29 2022-11-01 光大环境科技(中国)有限公司 Continuous sample injection waste plastic catalytic cracking oil production device and method
WO2024139623A1 (en) * 2022-12-29 2024-07-04 中国石油天然气股份有限公司 Waste plastic treatment method and device
GB2631198A (en) * 2022-12-29 2024-12-25 Petrochina Co Ltd Waste plastic treatment method and device

Similar Documents

Publication Publication Date Title
EP0747463B1 (en) Method for continuous liquefaction of waste plastics
AU2009295361B2 (en) Process and apparatus for decomposition of polymer products including those containing sulphur such as vulcanised rubber tyres and recovery of resources therefrom
JPH1190387A (en) Waste plastic dechlorination method and dechlorination equipment
JP3585637B2 (en) Catalytic cracking apparatus for synthetic polymer and method for producing oil using the same
WO2023223932A1 (en) Continuous organic matter pyrolysis device and continuous organic matter pyrolysis method
JP2002363337A (en) Plastic recycling method
JP2004035851A (en) Liquefaction apparatus
JP4768920B2 (en) Thermal decomposition of waste plastic
CN104471032A (en) Reactor for vaporizing and/or cleaning especially depolymerized plastic material and associated method
JP2013103998A (en) Waste plastic catalytic cracking liquefaction apparatus and catalytic cracking liquefaction method
JP2008163254A (en) Continuous apparatus for liquefying waste plastic into oil
JP3393057B2 (en) Continuous oiling equipment
JP2006056957A (en) Apparatus for converting waste plastic into oil
WO2020230157A1 (en) Device for melting plastic waste specifically for plastic pyrolysis
KR20170124980A (en) method of producing recycled fuel oil from waste synthetic resin
JP5678400B2 (en) Fluid tank, method for discharging solid particles from fluid tank, and method for treating workpiece
JPH10195451A (en) Melting and pyrolysis of waste plastic, its melting and pyrolizing tank and liquefaction of melted and pyrolized plastic
JPH0834978A (en) Method and apparatus for producing low boiling point hydrocarbon oil
CA2662118C (en) Process and apparatus for utilizing oxygen-containing polymers
JPH1129774A (en) Waste plastic thermal decomposition reactor
JP2000178376A (en) Dechlorination method and dechlorination equipment for mixed waste plastic
KR20210095327A (en) Melting apparatus for waste plastic processing
JPH06228569A (en) Method and equipment for decomposition of waste plastic
JPH0967581A (en) Method for removing hydrogen chloride from waste plastic containing vinyl chloride
JP2003096469A (en) Reductive oiling system for waste plastic

Legal Events

Date Code Title Description
A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20040330