JPH115868A - Recycling system of waste polystyrene resin by method for dissolving and decomposing to oil - Google Patents

Recycling system of waste polystyrene resin by method for dissolving and decomposing to oil

Info

Publication number
JPH115868A
JPH115868A JP19768297A JP19768297A JPH115868A JP H115868 A JPH115868 A JP H115868A JP 19768297 A JP19768297 A JP 19768297A JP 19768297 A JP19768297 A JP 19768297A JP H115868 A JPH115868 A JP H115868A
Authority
JP
Japan
Prior art keywords
solvent
polystyrene
oil
tank
light oil
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
JP19768297A
Other languages
Japanese (ja)
Inventor
Takashi Tachibana
孝 立花
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.)
AASU RECYCLE KK
Original Assignee
AASU RECYCLE KK
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 AASU RECYCLE KK filed Critical AASU RECYCLE KK
Priority to JP19768297A priority Critical patent/JPH115868A/en
Publication of JPH115868A publication Critical patent/JPH115868A/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
    • 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

PROBLEM TO BE SOLVED: To establish a recycle system of waste polystyrene by a method for dissolving and decomposing into oil. SOLUTION: Dissolving, melting, thermal decomposition of waste polystyrene into oil and light oil/heavy oil-separation of pyrolytically produced oil are carried out by effectively combining a simple screw machine, a thermal degradation tank (with an agitator and an electric heater) and a heat exchanger. The light oil having high dissolving ability to the polystyrene resin is used as a solvent and the light oil is used as a heat source for carrying out the melting and thermal decomposition by gasifying the light oil at a high temperature and directly contacting with the waste polystyrene. A multipurpose apparatus capable of carrying out a continuous separation of the light oil, which is a solvent, from the polystyrene resin and pelletizing the resin is provided by further adding a vacuum pump, a screw for discharging from the bottom of the thermal degradation tank, a cooling tank and a pelletizer. This apparatus is used as a core and dissolved waste polystyrene is recovered to the spot where the apparatus locates by putting the solvent (the light oil) obtained from the apparatus into a dissolving tank with a deodorizing device installed at a spot of occurrence of waste polystyrene to dissolve the waste polystyrene.

Description

【発明の詳細な説明】 [産業上の利用分野]本発明は廃ポリスチレン(発泡品
・トレー・容器)の発生場所である、市場・工場・スー
パー等に本溶媒を入れた溶解槽を設置し、その場で常温
で溶解し、高粘性の溶液をトラック等で収集、運搬後、
工場に設置されている溶媒回収装置(油化兼用)にて溶
媒とポリスチレン樹脂に分離して溶媒はそのまま再使用
する。又、ポリスチレン樹脂はペレット又は、成形品に
加工する一連の設備とリサイクルシステム(図−3参
照)に関する。
DETAILED DESCRIPTION OF THE INVENTION [Industrial application field] The present invention installs a dissolving tank containing this solvent in a market, a factory, a supermarket, etc., where waste polystyrene (foams, trays, containers) is generated. , Dissolve at room temperature on the spot, collect and transport highly viscous solution with trucks, etc.,
The solvent and polystyrene resin are separated by a solvent recovery device (also used for oiling) installed in the factory, and the solvent is reused as it is. Also, the polystyrene resin relates to a series of equipment for processing into pellets or molded products and a recycling system (see FIG. 3).

[従来の技術]廃ポリスチレン処理法として45%は再
資源化されていない(焼却・埋立)55%はマテリアル
再利用、溶融固化、ペレット化で再資源化される。その
うち、溶融固化が80%を占める。ポリスチレン樹脂は
熱可塑性を持っているので高熱をかけると柔らかくなり
やがて溶融する。加熱法として、蒸気、熱風、直接加
熱、赤外線摩擦熱法がある。本発明に近い方法として溶
媒方式がある。廃ポリスチレンは、その原材料であるス
チレンによく溶解する性質を利用し、溶解させ、これを
38℃、滞留時間3〜4時間与えて蒸発、熱分解させ、
さらに触媒を通して油化(スチレン液化)する方法。生
成油の全留分を溶媒として使用している。廃ポリスチレ
ン処理法の主流は溶融固化でコンスタントに多く発生す
る場所に設備を設け、製品価値として低いインゴットと
して引き取ってもらっている。本来は付加価値の高いバ
ージンペレットにして販売したいが、廃ポリスチレンの
中には異物(金属・アルミ・紙ラベル・石・他樹脂な
ど)が多く、数ミリ程度のペレットに加工する工程を妨
げてしまう。それらを除去する為には、高価な設備、多
くの人が必要となり、現法では経済性は全くない。他の
溶媒として柑橘系植物精油の「d−リモネン」,鉱物油
が使用されている。
[Prior Art] As a waste polystyrene treatment method, 45% is not recycled (incinerated and landfilled), and 55% is recycled by material reuse, melt solidification, and pelletization. Among them, melt solidification accounts for 80%. Polystyrene resin has thermoplasticity, so it becomes soft and melts when high heat is applied. Heating methods include steam, hot air, direct heating, and infrared friction heating. As a method close to the present invention, there is a solvent method. Waste polystyrene is dissolved by utilizing the property of dissolving it well in styrene, which is a raw material, and it is evaporated and thermally decomposed by giving it at 38 ° C. and a residence time of 3 to 4 hours.
In addition, a method of liquefying (styrene liquefaction) through a catalyst. All fractions of the product oil are used as solvent. The mainstream of the waste polystyrene treatment method is to install equipment in places where melting and solidification frequently occur, and have them receive ingots with low product value. Originally, we would like to sell high value-added virgin pellets, but waste polystyrene contains many foreign materials (metals, aluminum, paper labels, stones, other resins, etc.), which hinders the process of processing into pellets of several millimeters. I will. In order to remove them, expensive equipment and a large number of people are required, and there is no economic efficiency in the current method. As another solvent, citrus vegetable essential oil "d-limonene" and mineral oil are used.

[発明が解決すべき課題]従来法の問題点を列挙すると 1)発泡スチロール容器はカサ比重が非常に小さいので
もし減容なしで処理するなら広い蓄積場所と高い運搬
(空気を運ぶようなもの)コストがかかる。溶融固化設
備はスタートアップ時に人手・時間とエネルギーロスが
発生するので集中的処理を行うのが一般的である。その
為、処理する迄の広い保管場所が必要となる。
[Problems to be Solved by the Invention] To list the problems of the conventional method: 1) Styrofoam containers have a very small bulk specific gravity. If they are to be treated without volume reduction, they have a large storage area and high transportation (such as carrying air). )There will be a cost. Melting and solidifying equipment generally involves intensive processing because of the labor, time and energy loss that occurs during startup. Therefore, a large storage space until processing is required.

2)廃ポリスチレンの熱分解又は、接触分解生成油の全
留分(重質油を含む)を溶媒として使用する事は溶解能
力を下げ、かつ溶媒回収コストを高価なものとし回収し
たポリエチレン樹脂の品質を下げる。
2) Use of the entire fraction (including heavy oil) of the pyrolysis or catalytic cracking product oil of waste polystyrene as a solvent lowers the dissolving capacity, increases the cost of solvent recovery, and increases the cost of recovering the polyethylene resin. Reduce quality.

3)他の溶媒(d−リモネン)で廃ポリスチレンを溶解
させる時、100〜150℃に加熱する必要があり安全
上溶解する場所が限定される。又、他の溶剤コストは本
発明よりかなり高い。
3) When dissolving the waste polystyrene with another solvent (d-limonene), it is necessary to heat the polystyrene to 100 to 150 ° C., and the place where the polystyrene is dissolved is limited for safety. Also, other solvent costs are significantly higher than in the present invention.

4)廃ポリスチレンを溶融固化してから付加価値の高い
バージンペレットを造ることは前処理(選別・破砕・異
物除去・洗浄と乾燥)に大変なコストがかかり、現状で
は経済的に成り立たない。又、従来の溶融固化は高温で
行うのでポリスチレンの大幅な分子量低下で非常にグレ
ードの低い製品となっている。
4) Manufacturing high value-added virgin pellets after melting and solidifying waste polystyrene requires a great deal of pretreatment (sorting, crushing, foreign matter removal, washing and drying), and is not economically viable at present. Further, since the conventional melt-solidification is performed at a high temperature, the molecular weight of polystyrene is greatly reduced, so that the product has a very low grade.

5)溶媒を回収せず(リサイクルしない)常に熱分解の
みにたよる事は高い運転コストとなり、経済的に成り立
たない。
5) It is not economically feasible to always rely only on thermal decomposition without recovering (not recycling) the solvent, which results in high operating costs.

6)廃ポリスチレンがコンスタントに多く発生する場所
のみ、溶暉固化装置で処理されているが、少量しか発生
しない場所では産業廃棄物業者に高い処理費(運搬費が
高い)を支払って回収してもらっている。即ち、超小型
の溶融機がない為、少量発生個所での廃ポリスチレン回
収効率は低い。
6) Only the places where waste polystyrene is constantly generated abundantly are processed by the liquid consolidation equipment, but in places where only a small amount of waste polystyrene is generated, industrial waste traders pay high disposal costs (high transportation costs) to collect them. I have. That is, since there is no ultra-small melter, the waste polystyrene recovery efficiency at the place where a small amount is generated is low.

7)従来法でバージンペレット又は、成型品を造る時、
溶融する為に高価な押出機を使用する。
7) When making virgin pellets or molded products by conventional methods,
Use expensive extruders to melt.

8)廃ポリスチレンの熱分解油化の場合加熱炉管内コー
キング問題等があり長期安定運転は難しい。又多くが間
接加熱の為効率が悪くスケールアップがやりにくい。
8) In the case of thermal decomposition oil conversion of waste polystyrene, long-term stable operation is difficult due to coking problems in the heating furnace tube. In addition, many of them are indirectly heated, resulting in poor efficiency and difficult scale-up.

9)廃ポリスチレンの溶融,油化工程でスチレン臭等の
悪臭問題が未解決である。
9) The problem of malodor such as styrene odor has not been solved in the melting and oiling process of waste polystyrene.

以上、本発明は従来技術の問題点を全て解決することを
目的とする。
As described above, an object of the present invention is to solve all the problems of the related art.

[課題を解決する為の手段] 1)ポリスチレンの熱分解生成油はポリスチレンを溶解
する事は良く知られているが本法は溶解効率を上げるた
めに熱分解生成油を軽質油(蒸留範囲130〜170
℃,比重0.850),と重質油に分離し軽質油を溶媒
として使用する。分離法は蒸留塔なしで蒸発式熱交換器
を採用した。
[Means for Solving the Problems] 1) It is well known that a thermally decomposed oil of polystyrene dissolves polystyrene, but this method uses a light oil (distillation range 130 ~ 170
° C, specific gravity 0.850), and light oil is used as a solvent. The separation method employed an evaporative heat exchanger without a distillation column.

2)発泡スチロールの投入速度を上げる為,溶媒で溶解
後(1Lの溶媒に0.7KGポリスチレンが溶解)コロ
イド状になるまで溶かし込んでからポンプを介してスク
リュー機にフイードする。
2) In order to increase the charging rate of the polystyrene foam, after dissolving with a solvent (0.7 KG polystyrene is dissolved in 1 L of solvent), dissolve until it becomes colloidal, and feed it to a screw machine via a pump.

3)廃ポリスチレンには多くの異物(紙,魚,石,アル
ミ等)が含まれているためストレーナーで2段階処理
(一回目は溶解槽で二回目はスクリュー投入前)を行
う。
3) Waste polystyrene contains many foreign substances (paper, fish, stone, aluminum, etc.), so it is subjected to a two-stage treatment with a strainer (first time in a dissolution tank and second time before screw injection).

4)スクリュー機への熱供与は約350℃の軽質油ベー
パーをスクリュー側部より吹き込む。スクリューは多連
型,回転方向はギアによる外向回転で形状はリボンスク
リューが好ましい。軸の長さは約2Mである。樹脂温度
は約230℃に加熱される。
4) Heat is supplied to the screw machine by blowing light oil vapor at about 350 ° C. from the side of the screw. The screw is a multiple type, and the rotation direction is outward rotation by a gear, and the shape is preferably a ribbon screw. The length of the shaft is about 2M. The resin temperature is heated to about 230 ° C.

5)加熱溶融されたポリスチレン樹脂と軽質油は真空の
熱分解槽にフラッシュされポリスチレン樹脂と溶媒(軽
質油)に租分離される。ポリスチレン樹脂は熱分解槽底
部に設けられた攪拌翼と電気ヒーターにて混合,再加熱
されポリスチレン樹脂に溶解している溶媒はほとんど分
離し約97%回収される。
5) The heated and melted polystyrene resin and light oil are flushed to a vacuum pyrolysis tank and separated into polystyrene resin and a solvent (light oil). The polystyrene resin is mixed and reheated by an electric heater and a stirring blade provided at the bottom of the pyrolysis tank, and the solvent dissolved in the polystyrene resin is almost separated and about 97% is recovered.

6)分離された溶媒は熱交換器による熱回収と冷却器に
より液化されリサイクルされる。溶媒が不足したら熱分
解槽電気ヒーターにて380℃,4時間与えることによ
熱分解油が得られ蒸発式熱交換器にて軽質油/重質油に
粗分離される。
6) The separated solvent is heat-recovered by a heat exchanger and liquefied by a cooler and recycled. If the solvent is insufficient, the resultant is given at 380 ° C. for 4 hours with an electric heater in a pyrolysis tank to obtain pyrolysis oil, which is roughly separated into light oil / heavy oil by an evaporative heat exchanger.

7)スクリュー機内に吹き込まれる高温ガスは軽質油を
ポンプで昇圧後熱交換器と加熱炉で加熱する事により得
られる。この時管内脈動及びコーキング防止するために
蒸発式熱交換器を設け加熱炉入口は完全ベーパーとなる
ように(相変化無し)考慮されている。流体は軽質油で
あるので500℃の高温ガスにしてもコーキング問題は
クリアーされる。
7) The high temperature gas blown into the screw machine is obtained by heating the light oil with a heat exchanger and a heating furnace after increasing the pressure of the light oil with a pump. At this time, an evaporative heat exchanger is provided to prevent pulsation and coking in the tube, and the heating furnace inlet is considered to be completely vapor (no phase change). Since the fluid is light oil, the coking problem can be solved even with a high-temperature gas of 500 ° C.

8)熱分解ガス中には悪臭物質が濃縮してくるため加熱
炉にて焼却脱臭する。
8) Since the malodorous substance is concentrated in the pyrolysis gas, it is incinerated and deodorized in a heating furnace.

9)熱分解槽底部のポリスチレン樹脂は簡易スクリュー
機出口に多孔板を設け,紐状に押しだし冷却槽で急冷後
ペレタイザーで3〜5MMの長さに切断してペレットと
する。インゴットの場合は出口多孔板を取り除きそのま
ま冷却槽に落とし込む。
9) A polystyrene resin at the bottom of the pyrolysis tank is provided with a perforated plate at the outlet of a simple screw machine, extruded in a string form, quenched in a cooling tank, cut into a length of 3 to 5 MM with a pelletizer, and formed into pellets. In the case of an ingot, remove the perforated exit plate and drop it directly into the cooling tank.

10)本装置はコロイド状にしなくとも廃ポリスチレン
をスライド投入機を使用して400℃の高温ガスと接触
溶解溶融する。
10) The present apparatus uses a slide input machine to melt and dissolve waste polystyrene in contact with a 400 ° C. high-temperature gas without making it colloidal.

11)溶解槽は図−1の構造となっている。臭気対策と
して投入口開となれば小型ブロアーが自動的にスタート
し空気と臭気ガスを吸引しそのガスは冷凍機で冷却し臭
気成分を凝縮分離する。尚、レジンペレットを製造する
とき、着色ポリスチレンは品質価値を下げる為に溶解槽
へ投入の除選別しなければならない。着色ポリスチレン
が混入しても問題とならないのは射出成形機で着色剤を
使用する成形品製造の場合である。
11) The dissolution tank has the structure shown in Fig. 1. When the inlet is opened as a countermeasure against odor, the small blower starts automatically, sucks air and odor gas, and the gas is cooled by a refrigerator to condense and separate odor components. When producing resin pellets, the colored polystyrene must be sorted out in the dissolving tank in order to reduce the quality value. There is no problem even if the colored polystyrene is mixed in the case of manufacturing a molded article using a colorant in an injection molding machine.

[発明の効果] 1)発生した場所ですぐに溶解する事は集積エリアを小
さくする。
[Effects of the Invention] 1) Immediate dissolution at the place where it occurs reduces the accumulation area.

2)溶媒の原材料は廃ポリスチレンである。運転コスト
のかかる油化モードは一番初めの溶媒確保と補充用のみ
で通常は、運転コストのかからない溶媒回収モード(温
度230〜250℃蒸発操作のみ)オペレーションであ
る。熱分解モードでは、1バッチ6時間必要であるが溶
媒回収モードでは3時間で可能。溶媒製造コストは安く
なる。
2) The raw material of the solvent is waste polystyrene. The oiling mode, which requires an operating cost, is a solvent recovery mode (only at a temperature of 230 to 250 ° C. evaporating operation) in which only the initial solvent securing and replenishing is performed and no operating cost is required. In the thermal decomposition mode, one batch requires 6 hours, but in the solvent recovery mode, it can be done in 3 hours. Solvent production costs are lower.

3)溶媒の溶解能力は熱分解のみでは溶媒1リットル当
たりポリスチレンを0,6kg、熱分解・接触分解では
0,7kg溶解する。輸送効率は溶融と変わらない。
3) The solvent dissolving ability dissolves 0.6 kg of polystyrene per liter of solvent only by thermal decomposition, and dissolves 0.7 kg by thermal decomposition / catalytic decomposition. Transport efficiency is not different from melting.

4)発生した場所に設置する溶解槽の操作条件は常温
(加熱設備必要なし)、常圧であり、かつ火災、臭気対
策は十分とられている為、簡単な教育のみで誰でも投入
できる。本溶剤は引火点35℃以上に調整される為に消
防法は第2石油類に相当する。
4) The operating conditions of the dissolution tank installed in the place where it occurs are normal temperature (no heating equipment required), normal pressure, and sufficient measures against fire and odor are taken. Since this solvent is adjusted to a flash point of 35 ° C. or higher, the Fire Service Law corresponds to the second petroleum.

5)廃ポリスチレンの中には異物(金属、アルミ、紙、
砂、石、ガラス、野菜、魚、肉じる、他樹脂等)が多く
存在する。当然、溶解槽への投入者は異物除去に心掛け
なければならないが、もし誤って投入されたとしてもポ
リスチレンは溶媒で短時間で溶解し、高粘性の溶液とな
っていくが、他の異物は変化しないので、ストレーナー
を通すことにより異物のほとんどは除去され溶液(溶媒
+ポリエチレン)のみスクリュー機へ導入される。即
ち、従来法では異物を除去する為に、破砕、異物分離、
選別、洗浄、乾燥工程を必要としたが、本発明では溶液
として扱う事で上記工程は全て削除できる。高付加価値
製品であるバージンペレット(着色ポリスチレンは除
外)が経済的に製造可能となる。
5) Foreign matter (metal, aluminum, paper,
Sand, stone, glass, vegetables, fish, meat, other resins, etc.). Naturally, the person who puts it into the dissolution tank has to be careful in removing foreign matter, but even if it is mistakenly introduced, polystyrene will dissolve in a solvent in a short time and become a highly viscous solution. Since there is no change, most of the foreign matter is removed by passing through the strainer, and only the solution (solvent + polyethylene) is introduced into the screw machine. That is, in the conventional method, crushing, foreign matter separation,
Sorting, washing, and drying steps were required, but in the present invention, all of the above steps can be eliminated by treating them as a solution. Virgin pellets (excluding colored polystyrene), which are high value-added products, can be economically manufactured.

6)廃ポリスチレンを油化する場合、前処理設備(破砕
・減容)が必要であるが本発明ではそれら機器を全く必
要としない為に、非常に経済的である。
6) When the waste polystyrene is converted to oil, pretreatment equipment (crushing and volume reduction) is required, but the present invention does not require any such equipment, and is very economical.

7)溶媒の蒸留範囲は熱分解のみで130〜230℃熱
分解・接触分解で130〜190℃と軽い為低温度で溶
媒回収ができる回収条件は、常圧のとき、温度は230
〜250℃で回収率は、約90wt%圧力を減圧にすれ
ば、限りなく100%に近づく。軽質な溶媒を比較的低
温度で分離させるため(蒸留操作もなし)溶剤回収コス
トは低く,ポリスチレン樹脂への熱劣化は小さくでき、
最終製品であるペレット又は、成形品の品質は良い。又
1つの装置で油化(熱分解)と溶媒回収及びペレット製
造を兼ねるので設備費は安く効率的である。
7) The distillation range of the solvent is as low as 130 to 230 ° C for thermal decomposition only 130 to 190 ° C for pyrolysis and catalytic cracking. Therefore, the solvent can be recovered at low temperature.
At ~ 250 ° C, the recovery rate approaches 100% by reducing the pressure by about 90 wt% pressure. Since light solvents are separated at a relatively low temperature (no distillation operation), solvent recovery costs are low, and thermal degradation to polystyrene resin can be minimized.
The quality of the final product pellets or molded products is good. In addition, the equipment cost is low and efficient because one apparatus serves both oil conversion (pyrolysis), solvent recovery and pellet production.

8)発生した場所に設置する溶解槽は、構造が簡単であ
るから、超小型から大型まで容易に製作できる。特に超
小型で対応できる事は、廃ポリエチレン樹脂が発生する
あらゆる場所に設置でき、その結果、廃ポリスチレン回
収率は従来法より格段に改善される。
8) Since the dissolving tank installed at the place where the dissolution occurred has a simple structure, it can be easily manufactured from ultra-small to large. In particular, it can be installed in any place where waste polyethylene resin is generated, and as a result, the recovery rate of waste polystyrene is remarkably improved as compared with the conventional method.

9)本発明の廃ポリスチレンのリサイクルシステムを全
国に構築・拡大していけばスケールメリットが働き、市
場・工場・スーパーなどの処理費は従来より大幅に低下
する。又、家庭から排出されるゴミの中の発泡品、容器
類が減少するためにゴミのカサ比重が高くなり輸送効果
が改善される。
9) If the waste polystyrene recycling system of the present invention is constructed and expanded nationwide, economies of scale will work, and the processing costs for markets, factories, supermarkets, etc. will be significantly reduced. In addition, since the amount of foams and containers in the garbage discharged from the home is reduced, the bulk density of the garbage is increased, and the transport effect is improved.

10)従来法では、バージンペレット、成形品を造る
時、溶融するために高価な押出機を使用するが、本発明
は、溶媒回収槽の温度は、約230℃ありポリスチレン
樹脂は、完全に溶融している為、押出機は必要ない。簡
単なスクリュー機でよい。
10) In the conventional method, when manufacturing virgin pellets and molded articles, an expensive extruder is used for melting. However, in the present invention, the temperature of the solvent recovery tank is about 230 ° C. and the polystyrene resin is completely melted. Do not require an extruder. A simple screw machine is sufficient.

11)本法の熱供与は高温ガスを樹脂に直接接触させる
ためスケールアップが容易である。高温ガスの製造過程
ではコーキング等の問題は発生しない。なぜなら流体は
軽質油であり,脈動を防止するために還流熱交換器(蒸
発部付き)の設置,加熱炉管内は相変化のないよう入口
で完全ベーパーにしている。運転は安定している。
11) The heat donation of the present method is easy to scale up because the hot gas is brought into direct contact with the resin. No problems such as coking occur in the process of producing the high-temperature gas. Because the fluid is light oil, a reflux heat exchanger (with evaporator) is installed to prevent pulsation, and the inside of the heating furnace tube is completely vaporized at the inlet so that there is no phase change. Driving is stable.

12)廃ポリスチレンを溶融,熱分解するときスチレン
臭を発生するが完全にクローズで処理するため,又臭気
を含んだガスは加熱炉で焼却脱臭するため問題とならな
い。
12) When waste polystyrene is melted and thermally decomposed, styrene odor is generated, but it is not a problem because it is treated completely closed and gas containing odor is incinerated and deodorized in a heating furnace.

[実施例]以下本発明の実施例を図面に基づいて説明す
る。図−2は、本発明方法を実施するのに好適な装置の
概略構成図である。市場・工場・スーパー等で発生した
廃ポリスチレン(発泡品・容器)は,溶媒が1/2充填
された脱臭器付き溶解槽101に荒選別できる従業員に
よって投入される。溶解槽の溶液がコロイド状になれ
ば、トラツク(溶液槽と溶媒槽設置)に備えているポン
プ、ストレーナー102を通して、溶液をトラツクに積
み込む。次に溶媒をトラツクから溶解槽へ1/2充填す
る。溶液を積んだトラツクは工場(溶媒回収装置)へ行
き、再度ストレーナー105で異物を除去後、フィード
ポンプ104にてスクリュー機106へ導入する。溶剤
不足の時は、熱分解モードで運転するが、通常は溶剤回
収モードであるので、以下このモードで説明する。熱分
解槽108は、攪拌機110と電気ヒーター111を備
えており、真空下約230℃で運転する。スクリュー機
の加熱源は、溶媒と同じ留分を加熱炉フィードポンプ1
17で加熱炉118へフイードし300〜330℃迄昇
温しスクリュー機の側面109から直接吹き込んで熱の
供与と攪拌効果を与える。溶媒の蒸留範囲は130〜2
30℃であるので常圧でかなりの溶媒は、蒸発するが、
出来るだけ100%回収に近づけるために、熱分解槽は
真空状態で攪拌をかけながら電気ヒーターで再加熱を行
う。熱分解槽のポリスチレン樹脂中の油分は許容値以下
となる。分離された軽質油ガスは熱交換器112で熱回
収後,冷却されて液体となりリサイクルされる。又、溶
媒の一部は熱交換器112、加熱炉118で330℃に
加熱され、スクリュー機側面から吹き込まれる。熱分解
ガスと臭気物質は、ブロワー124で吸引されて加熱炉
で燃焼される。軽質油と水は比重差により分離される。
重質油は、加熱炉の燃料に使用される。熱分解槽に残っ
た約230℃のポリスチレン樹脂はスクリュー出口部に
取り付けられた多孔板121を通して紐状で押し出され
る。冷却槽122で固化し、これをペレタイザー123
により3〜5MM長さで切断してホッパーへ送り、袋詰
めし出荷される。
An embodiment of the present invention will be described below with reference to the drawings. FIG. 2 is a schematic configuration diagram of an apparatus suitable for carrying out the method of the present invention. Waste polystyrene (foamed products / containers) generated in markets, factories, supermarkets, etc. is put into a dissolving tank 101 with a deodorizer, which is half filled with a solvent, by employees who can roughly sort. When the solution in the dissolving tank becomes colloidal, the solution is loaded on the truck through a pump and a strainer 102 provided in the truck (installation of the solution tank and the solvent tank). Next, the solvent is half-filled from the truck into the dissolution tank. The truck loaded with the solution goes to a factory (solvent recovery device), where the foreign matter is removed again by the strainer 105 and then introduced into the screw machine 106 by the feed pump 104. When the solvent is insufficient, the operation is performed in the thermal decomposition mode. However, since the operation is usually in the solvent recovery mode, the operation will be described below in this mode. The pyrolysis tank 108 includes a stirrer 110 and an electric heater 111 and operates at about 230 ° C. under vacuum. The heating source of the screw machine uses the same fraction as the solvent as the heating furnace feed pump 1
At 17, the heat is fed to a heating furnace 118, the temperature is raised to 300 to 330 ° C., and blown directly from the side surface 109 of the screw machine to provide heat supply and a stirring effect. The distillation range of the solvent is 130-2
Since the temperature is 30 ° C, considerable solvent evaporates at normal pressure,
In order to achieve as close to 100% recovery as possible, the pyrolysis tank is reheated with an electric heater while stirring under vacuum. The oil content in the polystyrene resin in the pyrolysis tank is below the allowable value. After the separated light oil gas is recovered in the heat exchanger 112, it is cooled to become a liquid and recycled. A part of the solvent is heated to 330 ° C. in the heat exchanger 112 and the heating furnace 118 and is blown from the side of the screw machine. The pyrolysis gas and odorous substances are sucked by the blower 124 and burned in a heating furnace. Light oil and water are separated by the difference in specific gravity.
Heavy oil is used as fuel for heating furnaces. The polystyrene resin of about 230 ° C. remaining in the pyrolysis tank is extruded in a string form through a perforated plate 121 attached to the screw outlet. It is solidified in a cooling tank 122, and this is pelletized by a pelletizer 123.
And cut into 3-5 mm lengths, sent to the hopper, packed in bags and shipped.

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

【図−1】発明の廃ポリスチレン溶解槽の好ましい実施
形態を示す模型図である。
FIG. 1 is a model diagram showing a preferred embodiment of a waste polystyrene dissolving tank of the present invention.

【図−2】本発明の廃ポリスチレンの実施例を示す模型
図である。
FIG. 2 is a model diagram showing an example of waste polystyrene of the present invention.

【図−3】廃ポリスチレンリサイクルシステム図であ
る。
FIG. 3 is a diagram of a waste polystyrene recycling system.

【符号の説明】[Explanation of symbols]

101.溶解槽 101−a.投入口 101−b.冷凍分離器 101−c.吸引ブロアー 101−d.溶媒戻り管 101−e.投入口開閉スイッチ 102.ストレーナー1 103.ストックタンク 104.フイードポンプ 105.ストレーナー2 106.スクリュー機 107.スライド式投入機 108.熱分解槽 109.スクリュー機高温ガス吹き込み口 110.攪拌機 111.電気ヒーター 112.蒸発式熱交換器 113.冷却器 114.軽質油受槽 115.重質油受槽 116.熱分解ガス槽 117.加熱炉フイードポンプ 118.加熱炉 119.燃料油供給ポンプ 120.熱分解槽底スクリュー機 121.スクリュー機出口多孔板 122.冷却槽 123.ペレタイザー 124.吸引ブロアー ア 軽質油 イ 重質油 ウ 残査 エ ペレット オ インゴット 101. Dissolution tank 101-a. Input port 101-b. Freezing separator 101-c. Suction blower 101-d. Solvent return tube 101-e. Input port open / close switch 102. Strainer 1 103. Stock tank 104. Feed pump 105. Strainer 2 106. Screw machine 107. Sliding input machine 108. Pyrolysis tank 109. Screw machine hot gas injection port 110. Stirrer 111. Electric heater 112. Evaporative heat exchanger 113. Cooler 114. Light oil receiving tank 115. Heavy oil receiving tank 116. Pyrolysis gas tank 117. Heating furnace feed pump 118. Heating furnace 119. Fuel oil supply pump 120. Pyrolysis tank bottom screw machine 121. Perforated plate at screw machine outlet 122. Cooling tank 123. Pelletizer 124. Suction blower a Light oil b Heavy oil c Residue d Pellet o Ingot

─────────────────────────────────────────────────────
────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成10年1月5日[Submission date] January 5, 1998

【手続補正3】[Procedure amendment 3]

【補正対象書類名】図面[Document name to be amended] Drawing

【補正対象項目名】全図[Correction target item name] All figures

【補正方法】変更[Correction method] Change

【補正内容】[Correction contents]

【図−1】 FIG. 1

【図−2】 FIG. 2

【図−3】 [Figure-3]

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI C10G 1/10 ZAB B09B 3/00 302A 303E ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification code FI C10G 1/10 ZAB B09B 3/00 302A 303E

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】廃ポリスチレン(特に異物,汚れた発泡ス
チロール)を簡易スクリュー機,熱分解槽(攪拌機,電
気ヒーター付き),蒸発式熱交換器を有効に組み合わせ
る事により溶解,溶融,熱分解油化及び熱分解生成油の
軽質油/重質油の分離を行う。ポリスチレン樹脂に高い
溶解能力を持つ軽質油を溶媒とし又軽質油は高温ガス化
され廃ポリスチレンとの直接接触により溶融熱分解の熱
供給源として使用する。さらにその装置に真空ポンプ,
熱分解槽底抜き出し用スクリュー,冷却槽及びペレタイ
ザーを付加する事により連続的に溶媒とポリスチレン樹
脂の分離とペレット化が可能な多目的装置とする事を特
徴とする。
1. Melting, melting and pyrolysis of waste polystyrene (especially foreign matter and dirty polystyrene) by effectively combining a simple screw machine, a pyrolysis tank (with a stirrer and an electric heater), and an evaporative heat exchanger. And separation of light oil / heavy oil of the pyrolysis product oil. Light oil having high dissolving ability in polystyrene resin is used as a solvent, and the light oil is gasified at a high temperature and used as a heat source for melt pyrolysis by direct contact with waste polystyrene. In addition, a vacuum pump,
A multipurpose device capable of continuously separating and pelletizing the solvent and polystyrene resin by adding a screw for extracting the bottom of the pyrolysis tank, a cooling tank, and a pelletizer.
【請求項2】請求項−1の装置を核とし、そこから得ら
れる溶媒(軽質油)を,廃ポリスチレンの発生場所であ
る市場,工場,スーパー等に設けた脱臭器付きの溶解槽
に約1/2充填し常温のまま廃ポリスチレンを溶解槽に
投入しコロイド状迄溶解する。その溶液中の異物はスト
レーナーで除去後トラックに積み込み請求項−1の装置
まで運び,その装置で溶媒とポリスチレン樹脂に分離し
約97%の溶媒は回収されリサイクルされる。ポリスチ
レン樹脂はペレット又はインゴットとなる。これら一連
のリサイクルシステムと高効率な溶剤回収法及び溶解槽
設備について。
2. Using the apparatus of claim 1 as a core, a solvent (light oil) obtained therefrom is transferred to a dissolving tank with a deodorizer provided at a market, a factory, a supermarket or the like where waste polystyrene is generated. The waste polystyrene is put into a dissolving tank at a half filling and kept at room temperature, and dissolved until it becomes colloidal. Foreign matter in the solution is removed by a strainer, loaded on a truck, transported to the apparatus of claim 1, and separated into a solvent and a polystyrene resin by the apparatus. About 97% of the solvent is recovered and recycled. The polystyrene resin becomes a pellet or an ingot. A series of these recycling systems, highly efficient solvent recovery methods and dissolution tank facilities.
JP19768297A 1997-06-17 1997-06-17 Recycling system of waste polystyrene resin by method for dissolving and decomposing to oil Pending JPH115868A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP19768297A JPH115868A (en) 1997-06-17 1997-06-17 Recycling system of waste polystyrene resin by method for dissolving and decomposing to oil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP19768297A JPH115868A (en) 1997-06-17 1997-06-17 Recycling system of waste polystyrene resin by method for dissolving and decomposing to oil

Publications (1)

Publication Number Publication Date
JPH115868A true JPH115868A (en) 1999-01-12

Family

ID=16378599

Family Applications (1)

Application Number Title Priority Date Filing Date
JP19768297A Pending JPH115868A (en) 1997-06-17 1997-06-17 Recycling system of waste polystyrene resin by method for dissolving and decomposing to oil

Country Status (1)

Country Link
JP (1) JPH115868A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002180068A (en) * 2000-12-14 2002-06-26 Hoshun Tei Apparatus for forming waste plastic into oil
KR20020072889A (en) * 2001-03-13 2002-09-19 주식회사 지엘코리아유니언 the pyrolysis waste recycling method and system
KR100865466B1 (en) 2007-04-04 2008-10-28 한국화학연구원 Solvent Withdrawal Method and Apparatus For Reducing Volume Of Expanded Plastic Waste

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002180068A (en) * 2000-12-14 2002-06-26 Hoshun Tei Apparatus for forming waste plastic into oil
KR20020072889A (en) * 2001-03-13 2002-09-19 주식회사 지엘코리아유니언 the pyrolysis waste recycling method and system
KR100865466B1 (en) 2007-04-04 2008-10-28 한국화학연구원 Solvent Withdrawal Method and Apparatus For Reducing Volume Of Expanded Plastic Waste

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