JP2009084543A - Waste plastic liquefying apparatus - Google Patents

Waste plastic liquefying apparatus Download PDF

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JP2009084543A
JP2009084543A JP2007284363A JP2007284363A JP2009084543A JP 2009084543 A JP2009084543 A JP 2009084543A JP 2007284363 A JP2007284363 A JP 2007284363A JP 2007284363 A JP2007284363 A JP 2007284363A JP 2009084543 A JP2009084543 A JP 2009084543A
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oil
waste plastic
temperature
melting
plastic
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Yoshihiro Abe
良博 阿部
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RAMUSA ABE KK
Ramusa Abe KK
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RAMUSA ABE KK
Ramusa Abe KK
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/04Disintegrating plastics, e.g. by milling
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/04Disintegrating plastics, e.g. by milling
    • B29B2017/0424Specific disintegrating techniques; devices therefor
    • B29B2017/0496Pyrolysing the materials
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29CSHAPING OR JOINING OF PLASTICS; SHAPING OF MATERIAL IN A PLASTIC STATE, NOT OTHERWISE PROVIDED FOR; AFTER-TREATMENT OF THE SHAPED PRODUCTS, e.g. REPAIRING
    • B29C35/00Heating, cooling or curing, e.g. crosslinking or vulcanising; Apparatus therefor
    • B29C35/02Heating or curing, e.g. crosslinking or vulcanizing during moulding, e.g. in a mould
    • B29C35/08Heating or curing, e.g. crosslinking or vulcanizing during moulding, e.g. in a mould by wave energy or particle radiation
    • B29C35/0805Heating or curing, e.g. crosslinking or vulcanizing during moulding, e.g. in a mould by wave energy or particle radiation using electromagnetic radiation
    • B29C2035/0811Heating or curing, e.g. crosslinking or vulcanizing during moulding, e.g. in a mould by wave energy or particle radiation using electromagnetic radiation using induction
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29LINDEXING SCHEME ASSOCIATED WITH SUBCLASS B29C, RELATING TO PARTICULAR ARTICLES
    • B29L2030/00Pneumatic or solid tyres or parts thereof
    • 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

Abstract

<P>PROBLEM TO BE SOLVED: To attain liquefaction and oil extraction by continuous treatment with fusion pyrolysis even to an inclusion such as a mixture of different kinds of hydrocarbon-based, ester-based and chloride-based polymers with different shapes, sticking liquid and stain in containers, thermosetting plastic or non-waste plastic in waste plastic. <P>SOLUTION: A plurality of pyrolyzing machines 6 each with a high frequency induction heating coil provided around the outer periphery of an obliquely placed cylinder are juxtaposed, and waste plastic is submerged in dissolution oil stored in the pyrolyzing machine and melted. Floating matter and sediment are transferred pushing up the inclined surface while being stirred, and supplied to the following stage machine after draining oil. The melting-decomposing temperature of the following stage machine is set higher than the temperature of the upper stage machine, and the melting-decomposing temperature is further heightened in the final lower stage machine. Non-waste plastic and remaining carbon mixed in the waste plastic are removed, and oil steam pyrolyzed in each process is cooled to become oil, thus obtaining decomposition oil. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明はあらゆる廃プラスチックの混在物を燃料油としての再資源化を図るため、それぞれ異なった熱分解温度で熱分解油を製造する設備と方法に関する。  The present invention relates to equipment and a method for producing pyrolysis oil at different pyrolysis temperatures in order to recycle all waste plastic mixtures as fuel oil.

廃プラスチックの再資源化にあたり問題にされているのは分別分類である。金属ボルト等によって複合されていたり、容器のようにねじ締めされていたり、紐、帯、シート、使い捨てのカミソリ、ボールペン等用途によって形状は様々であり、使用箇所によってエステル系のみでなく塩素や窒素を含む合成樹脂等が混在状態で廃棄されている。  Sorting classification is a problem when recycling plastic waste. It is compounded by metal bolts, screwed like a container, string, band, sheet, disposable razor, ballpoint pen, etc., and the shape varies depending on the application, not only ester type but also chlorine and nitrogen Synthetic resin containing is discarded in a mixed state.

現在再資源化により再生されているのは主としてポリエステル系樹脂で我々の身近なものはペットボトルである。これすらキャップの取り除きから始まっているが、収集された容器はラベル除去、破砕、洗浄等の工程が必要になってくる。同一材料の選別は多くの人の手と時間を消費して再資源化が図られている。
もしこの中に異質の材料で構成された物質が混在すれば、再利用は阻止され不可能となる。
Currently, polyester resin is mainly recycled through recycling, and our familiar items are plastic bottles. Even this begins with the removal of the caps, but the collected containers require steps such as label removal, crushing, and washing. Selection of the same material is a resource-intensive process that consumes many people and time.
If substances made of different materials are mixed in this, reuse is prevented and impossible.

従来の廃プラスチック再資源化はエステル系ポリマーのみ必要であった。
特開2005−264104に開示されているように分別や裁断、洗浄等が必要となる。温度の違った熱分解により混入している塩化系の処理に於いては脱塩素が必要となる。
炭化水素系やエステル系、塩化系等の混在している廃プラスチックを融解熱分解させた廃プラスチック再生油は比重分類の提案がなされているが、前記処理廃プラスチックの混在比率に大きく左右される要素がある(特開2005−104095)。
Conventional waste plastic recycling required only ester polymers.
As disclosed in JP-A-2005-264104, sorting, cutting, cleaning, and the like are required. Dechlorination is required in the treatment of chlorinated compounds mixed by thermal decomposition at different temperatures.
Waste plastic recycled oil that has been obtained by melting and pyrolyzing waste plastics mixed with hydrocarbons, esters, chlorides, etc. has been proposed for specific gravity classification, but it depends greatly on the mixing ratio of the treated waste plastics. There are elements (Japanese Patent Laid-Open No. 2005-104095).

融解熱分解法に於いて分解油化させるには炭化水素プラスチック軽質油を抜き出すことが可能であるが、様々な不純物が混入した廃プラスチックに於いては融解温度が低いと融解油の粘度が高くなる。又、低温度領域に形成が始まり、特に低温液部に沈降して固形物となる。晶出する安息香酸やテレフタル酸は触媒を用いて除去している。  It is possible to extract hydrocarbon plastic light oil for cracking oil in the melt pyrolysis method. However, in waste plastic mixed with various impurities, if the melting temperature is low, the viscosity of the melted oil is high. Become. In addition, formation starts in a low temperature region, and in particular, settles into a low temperature liquid part to become a solid. Crystallized benzoic acid and terephthalic acid are removed using a catalyst.

結晶化または固形化する物質を高速回転させて結びつきを防止するには比較的低温の200℃〜250℃に於いて熱分解させ、分解しない軽質の廃プラスチックは共に混入している非廃プラスチック容器に付着しているアルミ箔のラベルまたは金属と共に次期行程に排出して分解温度を更に上げて融解・分解させる。最終工程に至って廃プラスチックを完全に熱分解させてカーボン状の残渣物と非廃プラスチックとを排出させ、ガス化させた油蒸気を冷却して再生油を回収する。
特開2005−104095 三菱マテリアル株式会社 特開2005−154518 石川島播磨重工業株式会社 特開2007−16245 株式会社東芝 特開平18−120113 新日本製鉄株式会社 特開平11−310659 千代田化工株式会社
A non-waste plastic container in which light waste plastic that is thermally decomposed at a relatively low temperature of 200 ° C. to 250 ° C. and is not decomposed is mixed together in order to prevent the bonding by rotating the material to be crystallized or solidified at high speed. It is discharged together with the aluminum foil label or metal adhering to the next step, and the melting temperature is further raised to melt and decompose. At the final step, the waste plastic is completely pyrolyzed to discharge carbon residue and non-waste plastic, and the gasified oil vapor is cooled to recover the regenerated oil.
JP-A-2005-104095 Mitsubishi Materials Corporation JP-A-2005-154518 Ishikawajima-Harima Heavy Industries Co., Ltd. JP2007-16245 TOSHIBA CORPORATION JP-A-18-120113 Nippon Steel Corporation JP 11-310659 Chiyoda Corporation

解決しようとする問題点は廃プラスチックが産業廃棄物であり多様な用途に使用されるため材質及び形状が多岐に渡り、その混在物の中には金属やアルミなどの付着物が混入し、炭化水素系やエステル系、塩化系等が混在しているのを一括して融解熱分解により燃料油への油化は可能か。  The problem to be solved is that waste plastics are industrial waste and are used for various purposes, so there are a wide variety of materials and shapes. In the mixture, deposits such as metal and aluminum are mixed and carbonized. Is it possible to convert oils to fuel oils by melting and pyrolysis of hydrogen, ester, and chlorinated substances at once?

本発明は廃プラスチックが異なる材質や非プラスチックが混在していて分類、選別することは不可能であるのを、混在した状態でそのまま一括して溶解油に浸漬させ、未融解・未分解プラスチックと非プラスチックとを共に排出させて次期熱分解機に供給し、次期熱分解機では初期の分解温度よりも高い温度で前記作業を行う。一次工程も二次工程も三次工程も共に同じ熱分解作業を行うが、それぞれ一次よりも二次、二次よりも三次と順次分解温度を上げて熱分解させ、それぞれの工程で熱分解した廃プラスチックの油蒸気は熱交換器により凝縮、液化させる。  In the present invention, it is impossible to classify and sort waste plastics with different materials or non-plastics. The non-plastic is discharged together and supplied to the next pyrolyzer, which performs the above operation at a temperature higher than the initial cracking temperature. The primary pyrolysis process, the secondary process, and the tertiary process are the same, but the waste is decomposed by increasing the decomposition temperature sequentially from the primary to the secondary, and from the secondary to the tertiary. Plastic oil vapor is condensed and liquefied by a heat exchanger.

本発明は混在する炭化水素系やエステル系、塩化系等のポリマーの混在下に於いて廃プラスチックを従来のように選別することは不可能なため、選別することなく混在のまま一括して熱分解を行う。
混在する廃プラスチックによって分解温度が大幅に異なるため、分解温度差を利用して熱分解させる。
In the present invention, it is impossible to sort waste plastic as usual in the presence of mixed hydrocarbon, ester, and chloride polymers. Disassemble.
Since the decomposition temperature varies greatly depending on the waste plastics that are mixed, thermal decomposition is performed using the difference in decomposition temperature.

すべての廃プラスチックの混在物は分解温度を変更させることにより全て熱分解、気化させて冷却油化させ、残渣物を除去した熱分解油を実現した。  All waste plastic inclusions were pyrolyzed and vaporized by changing the decomposition temperature, and the oil was made into cooling oil.

図1は本発明装置の1実施例の装置側面図であって、仮想線内の機構を1グループとして左上のものを仮にAグループとすると、更に順次Bグループ、Cグループと配置する。
機構を説明すると符号1.は投入ホッパーの投入ゲートであり、分解工程中は1.、2.のゲートは閉である。原料である廃プラスチックを供給するには1.を開、2.を閉の状態で3.受入ホッパーに廃プラスチックを供給し、1.ホッパーゲート閉に於いて4.吸気口よりのエジェクターでの吸引によって無酸素状態を作り出す。
FIG. 1 is a side view of an apparatus according to an embodiment of the present invention. If the mechanism in the phantom line is one group and the upper left one is assumed to be A group, B group and C group are further arranged sequentially.
The mechanism will be described with reference to 1. Is a charging gate of the charging hopper. 2. The gate of is closed. To supply waste plastic as a raw material 1. Open In the closed state. Supply waste plastic to the receiving hopper. 3. When the hopper gate is closed Anaerobic conditions are created by suction with an ejector from the air intake.

2.ホッパー下部供給ゲートを開き、6.熱分解機に廃プラスチックを落下供給させる。供給後は前記2.ゲートを閉じる。
10.は前もって収容させた溶解油であり、廃プラスチック投入後に常温より目的温度の200℃まで昇温させても良いし、あらかじめ融解・分解作業以前に目的温度に到達させておいても良い。
この220℃程度の温度ではビニールシート袋、紐、テープ、ペットボトル等の融解・分解に適す。
2. Open the lower hopper supply gate, 6. Drop the waste plastic into the pyrolyzer. After the supply, 2. Close the gate.
10. Is dissolved oil stored in advance, and may be raised from normal temperature to 200 ° C. after throwing in the waste plastic, or may be reached in advance before melting / decomposing work.
This temperature of about 220 ° C. is suitable for melting / decomposing plastic sheet bags, strings, tapes, plastic bottles and the like.

前記のように比較的低温油化の工程では物理的に重合している。ペットボトルのキャップとねじが嵌合されていると融解速度は遅い。
220℃程度の加熱により塩化系の塩素が少し脱塩素し始める。
6.熱分解機の外周に5.高周波誘導加熱コイルを巻きつけて外周より加熱させ、内部には撹拌軸と撹拌羽根、羽根間を接合させた廃プラスチック浸漬羽根と未融解物を排出方向に送る送り羽根を設け、11.ギヤードモートルにて回転を与える。
As described above, physical polymerization is performed in the relatively low temperature oiling step. When the bottle cap and screw are fitted, the melting speed is slow.
Chlorine-based chlorine begins to dechlorinate a little by heating at about 220 ° C.
6). 4. around the pyrolyzer 10. A high frequency induction heating coil is wound around and heated from the outer periphery, and a stirring shaft and a stirring blade, a waste plastic immersion blade joined between the blades, and a feed blade for sending unmelted material in the discharge direction are provided. Giving rotation with a geared motor.

前記熱分解機は円筒状のフレームの外周に高周波誘導加熱コイルを巻いて断熱を施し、コイル自体の過熱を防止するためその内部に通水させたIHである。
熱分解機フレームは排出側を水上とし廃プラスチック供給側を水下側になるように傾斜させ、内部に収容した溶解油に融解物を全量油浴させてゆっくりと撹拌を与えながら斜路を送り羽根によって水上に向かって移動させる。
The pyrolyzer is an IH in which a high-frequency induction heating coil is wound around the outer periphery of a cylindrical frame to provide heat insulation, and water is passed through the coil to prevent overheating of the coil itself.
The pyrolyzer frame is tilted so that the discharge side is on the water and the waste plastic supply side is on the bottom, and the melted oil is fully bathed in the dissolved oil contained in it, and the slant is sent while slowly stirring the blade. Move it towards the water.

融解温度が低いため融解しない廃プラスチックや、金属片が付属した使い捨てカミソリ、容器類のアルミ片、陶器、ガラス等の廃プラスチックに混入した異質物の破片は熱分解機フレームに沈降する。廃プラスチック中未融解の熱硬化性廃プラスチックと塩化系廃プラスチックは溶解油液面に浮上し、共に排出側に向かって送り羽根により移動される。  Waste plastic that does not melt due to its low melting temperature, and disposable razors with metal pieces, aluminum pieces in containers, pieces of foreign materials mixed in waste plastic such as ceramics and glass settle on the pyrolyzer frame. The unmelted thermosetting waste plastic and chlorinated waste plastic in the waste plastic float on the surface of the dissolved oil, and both are moved toward the discharge side by feed blades.

斜置した熱分解機フレーム内の溶解油はフレームの排出口手前付近までしか無いため、撹拌軸もフレームの排出先端斜部も共に溶解油に接せずに斜路である円筒は油切りの作用をなし、未融解廃プラスチックと非廃プラスチックは油切りされて8排出口上部ゲートのシュート部に集まる。  Since the melted oil in the frame of the pyrolyzer installed in the oblique direction is only near the front of the discharge port of the frame, neither the stirring shaft nor the slanted portion of the discharge end of the frame is in contact with the dissolved oil. The unmelted waste plastic and non-waste plastic are drained and gathered at the chute of the upper gate of the eight outlets.

融解・分解作業の間に熱分解した油蒸気は熱分解機斜め上部空間の溶解油液面に於いて蒸発して7.排気口より吸引され、吸引ガスは14.サイクロン型熱交換器に於いて冷却されて油滴を集合し、油液となってプラスチック分解油として回収される。  The oil vapor pyrolyzed during the melting and decomposing operation evaporates at the dissolved oil level in the oblique upper space of the pyrolyzer. The suction gas is sucked from the exhaust port. In the cyclone type heat exchanger, the oil droplets are collected by cooling and collected as a plastic decomposition oil as an oil liquid.

プラスチック分解油は混入した塩素ガス等の異臭が生じる。又、炭化水素系、エステル系等も軽い異臭を排気する。消臭又は中和をさせて異臭の低減を図る。
本発明の装置では消臭を目的としてアルカリ系の炉材に吸着させる21.消臭塔に通し、22.水タンク内に設置した23.エジェクターポンプにより熱分解機内からポンプの間を負圧として24.水面上より大気中にガスを放出させる。
Plastic cracked oil has a bad smell such as mixed chlorine gas. Also, hydrocarbons, esters and the like exhaust light off-flavors. Deodorize or neutralize to reduce off-flavors.
In the apparatus of the present invention, it is adsorbed to an alkaline furnace material for the purpose of deodorization. Passing through deodorant tower, 22. Installed in water tank 23. 24. A negative pressure is generated between the inside of the pyrolyzer by the ejector pump. Release gas from the surface of the water into the atmosphere.

廃プラスチックの未融解物と非廃プラスチックは8.排出口上部ゲートが開かれて9.排出口下部ゲートとの間に止まり、更に上部ゲートを閉じて下部ゲートを開放すると段々状に設置した次期の熱分解機に収容され、収容が終わると上部ゲートも下部ゲートも共に閉として融解・分解作業を行う。
前記Aグループ、次設したBグループ、また次のCグループと融解・分解工程を連続して実施した。
8. Unmelted waste plastics and non-waste plastics 8. The upper discharge gate is opened. When the upper gate is closed and the lower gate is opened, it is stored in the next pyrolyzer installed in stages, and when the storage ends, both the upper gate and the lower gate are closed and melted. Perform disassembly work.
The melting / decomposing process was continuously carried out with the A group, the next established B group, and the next C group.

次設であるBグループはAグループで融解・分解しなかった廃プラスチックの未処理物のため融解温度を上げて400℃以上450℃程度に設定して、前記Aグループで実施した工程を再実施する。
Bグループの融解・分解工程でも未融解廃プラスチックと再度硬化して生成した廃プラスチックが撹拌羽根で細分化される。
The next group, Group B, is an untreated waste plastic that was not melted or decomposed in Group A, and raised the melting temperature to 400 ° C to 450 ° C. To do.
In the melting / decomposition process of Group B, the unmelted waste plastic and the waste plastic produced by curing again are subdivided by the stirring blades.

消しゴム状に生成する結晶性有機物はAグループBグループとも発生する。
融解・分解温度の上昇に於いて結晶性有機物の量は減少する。400℃以上450℃程度での未融解・未分解物は再度Cグループに供給させて溶解油に浸漬させ、さらに融解・分解温度を上げて融解・分解させると、混入した紙片は炭化する。
The crystalline organic matter generated in the form of an eraser is generated in both the A group and the B group.
As the melting and decomposition temperature increases, the amount of crystalline organic matter decreases. When unmelted and undecomposed matter at 400 ° C. or higher and about 450 ° C. is supplied again to Group C, immersed in dissolved oil, and further melted / decomposed at a higher melting / decomposition temperature, the mixed paper piece is carbonized.

Cグループで昇温融解させると熱硬化性廃プラスチックも塩化系廃プラスチックも全て融解し油化するが、採油した油液を常温下で放置すると油液中に一部が固形化する。
残渣物は炭化し、塩化系の残渣物は多孔化し軽質化した炭化物が生成する。
分解温度は580℃前後が良い。全ての未分解物は12.残渣物容器に混同して排出される。
When the temperature is melted in Group C, both the thermosetting waste plastic and the chlorinated waste plastic are melted and converted into oil. However, when the collected oil is left at room temperature, a part of the oil is solidified in the oil.
The residue is carbonized, and the chlorinated residue is made porous and lightened.
The decomposition temperature is preferably around 580 ° C. All undegraded products are 12. It is confused and discharged to the residue container.

本発明の特長は1段、2段、3段と上下に熱分解機を重設させ、傾斜を設けることで溶解油への浸漬によって未融解物の表面に付着した油分を分離させながら斜面を送り上げることが可能である。
蒸散油気は設備全てが真空であり、Aグループの受入ホッパーでの真空引きからBグループCグループと12.残渣物容器とが連通していて、更に残渣物容器にも4吸気口を設けて真空引きしているためすべて皆真空である特長を有する。
The feature of the present invention is that the pyrolyzer is placed one above the other in the first, second, and third stages, and the slope is formed while separating the oil adhering to the surface of the unmelted material by immersion in the dissolved oil by providing an inclination. It is possible to feed up.
All the equipment of the transpiration oil is vacuum, and from the evacuation with the receiving hopper of the A group, the B group C group and 12. Since the residue container is in communication with each other, and the residue container is provided with four air inlets and is evacuated, all the components have a vacuum.

熱分解機より発生する油蒸気は図2に示す外形図の14.サイクロン型熱交換器の16.吸入口より吸入され、サイクロン型熱交換器は胴体外周に19.冷却水を通し、冷却された油蒸気は液化して18.採油タンクに収容される。20.脱臭ろ過材はアルカリ質のセラミックを充填させたものを21.消臭塔の内部に収容する。ろ過材はPH12以上の多孔質状物質を充填させる。障害物と吸引ガスの遅延を計って23.エジェクターポンプで吸引させ、24.水封させた水中を通過させて大気に放出させる。  The oil vapor generated from the pyrolyzer is 14. 16. Cyclone heat exchanger The cyclone type heat exchanger is inhaled at the outer periphery of the fuselage. Cooling water vapor is liquefied by passing cooling water and 18. Housed in oil collection tank. 20. 21. Deodorizing filter medium filled with alkaline ceramic. Store inside the deodorant tower. The filter medium is filled with a porous substance having a pH of 12 or more. 23. Measure the delay of obstacles and suction gas. Suction with an ejector pump, 24. Pass through water-sealed water and release to the atmosphere.

本発明は廃プラスチック中に混在する紙片、アルミ箔、ゴム類、針金、金属類等の混入混在物を選別せずに、また廃プラスチックの種別を問わずに加熱油化させるものである。  In the present invention, the oil mixture is made into a heating oil regardless of the type of the waste plastic without sorting out mixed materials such as paper pieces, aluminum foil, rubbers, wires, metals and the like mixed in the waste plastic.

採油した油は低温での熱分解ほど粘度が低く、高温ほど油の重量が重い。重い油を分解油としての利用は可能である。
高周波誘導加熱の利点は融解・分解温度の設定が自由に可能であり、あらゆる混入混在物に対処できる。
The oil collected has a lower viscosity as the heat decomposes at a lower temperature, and the weight of the oil increases as the temperature increases. Heavy oil can be used as cracked oil.
The advantage of high-frequency induction heating is that the melting / decomposition temperature can be set freely, and it is possible to deal with any mixed substances.

本廃プラスチック熱分解機の特徴は、斜め置きしたフレームの外周より高周波により加熱させて溶解油に伝熱させ、撹拌羽根と浸漬羽根により溶解油中に強制的に押し込む。
融解温度不足により未融解物及び非廃プラスチックはゆっくりと送り羽根により斜面を上昇し、溶解油液面を離れると室温が高いため蒸発と融解作用により付着油は滴下し、斜面を流下して溶解油に戻る。
未融解物と異物の付着油は油切りされる効果がある。
A feature of this waste plastic pyrolyzer is that it is heated at a high frequency from the outer periphery of a frame placed obliquely to transfer heat to the dissolved oil, and is forced into the dissolved oil by a stirring blade and an immersion blade.
Due to insufficient melting temperature, unmelted materials and non-waste plastics slowly rise up the slope by the feed blade, and when leaving the dissolved oil surface, the room temperature is high, so the adhering oil drops due to evaporation and melting action, and flows down the slope and dissolves. Return to oil.
Unmelted and foreign oil deposits have the effect of draining.

本発明の廃プラスチック熱分解機に於いてテストする。
処理物は買い物袋、ビニールシート、紐、帯、バンド、各種容器を20kg投入し、設定温度の250℃に昇温15分、融解維持時間5分で溶解油は古タイヤよりの乾留油を使用。残渣物は少量、採油量は87%。
Test in the waste plastic pyrolyzer of the present invention.
20 kg of shopping bags, vinyl sheets, strings, bands, bands, and various containers are put into the treated items, the temperature is raised to 250 ° C. for 15 minutes, and the melting oil is maintained for 5 minutes. . Small amount of residue and 87% oil collection.

前記テスト機において前記溶解油を用いて実施。
テスト温度は350℃で30分間。
上記と同じ処理物と熱硬化性の溶接ワイヤーリール、古タイヤを投入。
採油量は重量比で42%。残渣物は結晶物の消しゴム状固形物。
Performed using the dissolved oil in the test machine.
The test temperature is 350 ° C for 30 minutes.
The same processed material, thermosetting welding wire reel, and old tires are introduced.
The amount of oil collected is 42% by weight. The residue is a crystalline eraser-like solid.

テスト機は同じで溶解油は前回の残油に、補充した処理物は100A〜150AのVAフランジ、エルボー、パイプ等塩化ビニル廃プラスチック。
テスト温度550℃で30分経過、採油量は重量比で61%。
油化後の残渣物は多孔質で軽石状の黒色カーボン状物質となる。
The test machine is the same, the dissolved oil is the previous residual oil, and the replenished processed material is 100A-150A VA flange, elbow, pipe and other vinyl chloride waste plastics.
The test temperature was 550 ° C. for 30 minutes, and the amount of oil collected was 61% by weight.
The residue after liquefaction becomes a porous, pumice-like black carbon-like substance.

本発明装置の1実施例の熱分解機の設置側面図である。It is the installation side view of the thermal decomposition machine of one Example of this invention apparatus. 本発明装置のサイクロン型熱交換器と消臭装置を示した図である。It is the figure which showed the cyclone type heat exchanger and deodorizing apparatus of this invention apparatus. 本発明装置の熱分解機と採油・消臭装置を示した図である。It is the figure which showed the thermal decomposition machine of this invention apparatus, and oil-collecting / deodorizing apparatus.

符号の説明Explanation of symbols

1 投入ホッパー投入ゲート
2 ホッパー下部供給ゲート
3 受入れホッパー
4 吸気口
5 高周波誘導加熱コイル
6 熱分解機
7 排気口
8 排出口上部ゲート
9 排出口下部ゲート
10 溶解油
11 ギヤードモートル
A 以上の機構を総称してAグループ
B 5〜11の機構を総称してBグループ
C 5〜11の機構を総称してCグループ
12 残渣物容器
13 排出残渣物
14 サイクロン型熱交換器
15 サイクロン内筒
16 サイクロン吸入口
17 消臭装置吸入口
18 採油タンク
19 冷却水
20 脱臭ろ過材
21 消臭塔
22 水タンク
23 エジェクターポンプ
24 水
A′ Aグループに付随する14〜24の機構を総称してA′グループ
B′ Bグループに付随する14〜24の機構を総称してB′グループ
C′ Cグループに付随する14〜24の機構を総称してC′グループ
DESCRIPTION OF SYMBOLS 1 Input hopper input gate 2 Hopper lower supply gate 3 Receiving hopper 4 Intake port 5 High frequency induction heating coil 6 Thermal decomposition machine 7 Exhaust port 8 Discharge port upper gate 9 Discharge port lower gate 10 Dissolved oil 11 Geared motor A The mechanism of A group B 5-11 is named generically and the mechanism of B group C 5-11 is generically called C group 12. Residue container 13 Discharge residue 14 Cyclone heat exchanger 15 Cyclone inner cylinder 16 Cyclone inlet 17 Deodorizing device suction port 18 Oil collection tank 19 Cooling water 20 Deodorizing filter medium 21 Deodorizing tower 22 Water tank 23 Ejector pump 24 Water A ′ A group A ′ group B ′ B 14 to 24 mechanisms associated with the group are collectively referred to as 14 to 24 mechanisms associated with the B 'group C' C group. C 'group are collectively referred to as structure

Claims (2)

円筒フレームに高周波誘導加熱コイルを周設して傾斜横置きさせ、溶解油を収容した内部に軸と撹拌羽根と浸漬羽根と送り羽根を設け、傾斜フレーム高位置側に排気口と背面に排出口、低位置側には供給口と給油口とで構成するグループを複数段差状に重設し、上段の分解温度より下段に至るほど高温によって分解させる廃プラスチック熱分解機。  A high-frequency induction heating coil is placed around the cylindrical frame and placed horizontally, and the shaft, stirring blade, immersion blade, and feed blade are provided inside the melted oil. A waste plastic pyrolyzer with a plurality of steps consisting of a supply port and a fuel supply port stacked on the low position side, and decomposed at higher temperatures from the upper decomposition temperature to the lower one. 円筒フレームの傾斜により油切りを可能とし、各グループ間の供給口と排出口と残渣物容器とを連通させて負圧を維持させた前記請求項1の熱分解機。  2. The pyrolyzer according to claim 1, wherein oil can be removed by inclining the cylindrical frame, and the negative pressure is maintained by communicating the supply port, the discharge port and the residue container between the groups.
JP2007284363A 2007-10-02 2007-10-02 Waste plastic liquefying apparatus Pending JP2009084543A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107586556A (en) * 2017-09-30 2018-01-16 济南恒誉环保科技股份有限公司 A kind of technique and system for preventing excessive fragmentation
JP2021023919A (en) * 2019-08-05 2021-02-22 阿部 良博 Non-activation device
KR20220122378A (en) * 2021-02-26 2022-09-02 권수길 Continuous powered thermal decomposition emulsifier
KR102596791B1 (en) * 2022-11-22 2023-11-01 주식회사동서산업롤 Waste plastic emulsification system with improved heating and reduction efficiency

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107586556A (en) * 2017-09-30 2018-01-16 济南恒誉环保科技股份有限公司 A kind of technique and system for preventing excessive fragmentation
JP2021023919A (en) * 2019-08-05 2021-02-22 阿部 良博 Non-activation device
JP7390568B2 (en) 2019-08-05 2023-12-04 阿部 荒喜 deactivation device
KR20220122378A (en) * 2021-02-26 2022-09-02 권수길 Continuous powered thermal decomposition emulsifier
KR102529219B1 (en) 2021-02-26 2023-05-04 권수길 Continuous powered thermal decomposition emulsifier
KR102596791B1 (en) * 2022-11-22 2023-11-01 주식회사동서산업롤 Waste plastic emulsification system with improved heating and reduction efficiency

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