JP4804115B2 - Method for separating mixed plastics - Google Patents

Method for separating mixed plastics Download PDF

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JP4804115B2
JP4804115B2 JP2005321998A JP2005321998A JP4804115B2 JP 4804115 B2 JP4804115 B2 JP 4804115B2 JP 2005321998 A JP2005321998 A JP 2005321998A JP 2005321998 A JP2005321998 A JP 2005321998A JP 4804115 B2 JP4804115 B2 JP 4804115B2
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water
plastic
stirring tank
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JP2007125520A (en
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幸三 樋田
和正 水野
実 中島
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Teijin Ltd
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    • 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
    • Y02W30/52Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly
    • 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

Description

本発明は複合素材からなるプラスチックの分別に関し、特に再利用を目的とする一般及び産業廃棄物中のペットボトル屑に含まれるポリプロピレン及び/又はポリエチレンなどの軽質プラスチック、及びポリエチレンテレフタレートなどのポリエステル系プラスチックの比重分離による混合プラスチックの分別方法に関する。   The present invention relates to the separation of plastics composed of composite materials, and in particular, light plastics such as polypropylene and / or polyethylene contained in PET bottle waste in general and industrial waste for reuse, and polyester plastics such as polyethylene terephthalate. The present invention relates to a method for separating mixed plastics by specific gravity separation.

資源保護のため、廃棄物から再利用可能な資源を回収し、しかるべき処理を施して再び役立てること、すなわちリサイクルは現代社会における極めて重要な課題である。なかでもプラスチック類は有限の資源である石油を主原料とする上、廃棄物として処理するにも多くの環境問題を発生しやすく、リサイクルの重要性が大きい。比較的選別収集の進んでいるペットボトルなどを含め廃プラスチック類は、食品、化粧品、洗剤等の容器類として使用されたものの閉める割合が大きい。これらペットボトルなどはキャップ部分に軽質プラスチック類であるポリプロピレン及び/又はポリエチレンが、また、ラベルなどにはポリエチレン及びポリスチレンが多く使用されている。リサイクルする上ではこれらのプラスチックを効率的に、高精度に分別する必要があり、リサイクル活動を進めていく上で分別精度と回収率を両立させることのできる技術が要望されている。   In order to protect resources, recyclable resources are collected from waste, treated appropriately, and reused, that is, recycling is an extremely important issue in modern society. In particular, plastics are made from petroleum, which is a finite resource, as a main raw material, and are prone to many environmental problems when treated as waste, so recycling is very important. Waste plastics, including PET bottles, which have been relatively sorted and collected, have a large percentage of closure of those used as containers for food, cosmetics, detergents, and the like. In these PET bottles, polypropylene and / or polyethylene, which are light plastics, are used for the cap portion, and polyethylene and polystyrene are often used for labels and the like. In recycling, it is necessary to sort these plastics efficiently and with high precision, and there is a demand for a technology that can achieve both separation precision and a recovery rate in the course of recycling activities.

プラスチックの複合素材を単一素材に分別する方法として気体流を利用した比重選別で分離する方法(例えば特許文献1参照。)が公知であるが、気体中では分別したプラスチックの純度は60〜70%程度にとどまり、バージン材としてリサイクルすることが困難である。また、比重が1.0を超えるプラスチックと1.0未満のプラスチックの分別方法として開放水槽にプラスチックを投入し、沈降したものと浮遊したものに分離する方法(例えば特許文献2、3参照。)では、比重が1.0を超過するポリスチレン、ポリエステルが混在している場合には両者を分別することが困難である。 As a method of separating a composite material of plastic into a single material, a method of separating by specific gravity selection using a gas flow (for example, see Patent Document 1) is known, but the purity of the plastic separated in gas is 60 to 70. It is difficult to recycle as a virgin material. In addition, as a method for separating plastic having a specific gravity of more than 1.0 and plastic having a density of less than 1.0 , a method of putting plastic into an open water tank and separating it into a settling and floating one (see, for example, Patent Documents 2 and 3). Then, when polystyrene and polyester having a specific gravity exceeding 1.0 are mixed, it is difficult to separate them.

更に、上下に排水口を有する円筒形状の液体が充満された選別装置内の中央に廃プラスチックの水スラリーを供給し、旋回流により旋回しながら上昇流及び下降流により上部排出口から低比重プラスチックを下部排出口から高比重プラスチックを回収する方法(例えば特許文献4参照。)も提案されているが液成分の下降流が存在する為、液流れにより主に高比重プラスチックの純度を99%以上にアップさせることは現実的には困難であり、また、低流速範囲であることから大規模処理をする際には非常に大きな設備が必要となるなどの問題がある。これらとは別に、液体サイクロン形状を持つ液体比重分離機により廃プラスチックの水スラリーから単一素材のプラスチックに分別する案(例えば特許文献5参照。)も提案されている。しかし、これらの設備は一般に処理可能量が小さなものが多く、大規模な処理量に対応できないため、処理量が増加する場合には多系列分離装置を設置する必要があり、経済的とはいえないという欠点もある。   In addition, the waste plastic water slurry is supplied to the center of the sorting device filled with a cylindrical liquid with drainage ports at the top and bottom, and the low specific gravity plastic is fed from the upper discharge port by the upward and downward flow while swirling by the swirl flow. A method of recovering high specific gravity plastic from the lower discharge port (see, for example, Patent Document 4) has also been proposed, but since there is a downward flow of liquid components, the purity of the high specific gravity plastic mainly exceeds 99% due to the liquid flow. In reality, it is difficult to increase the flow rate, and since it is in the low flow rate range, there is a problem that a very large facility is required for large-scale processing. In addition to these, there has also been proposed a method (for example, see Patent Document 5) in which a liquid specific gravity separator having a liquid cyclone shape separates waste plastic water slurry into a single material plastic. However, these facilities generally have a small processable amount and cannot handle a large amount of processing, so if the processing amount increases, it is necessary to install a multi-sequence separation device, which is economical. There is also a drawback of not.

特開平6−63941号公報(特許請求の範囲)Japanese Patent Laid-Open No. 6-63941 (Claims) 特開昭48−100760号公報(特許請求の範囲)Japanese Patent Laid-Open No. 48-1000076 (Claims) 特開平4−326955号公報(特許請求の範囲)JP-A-4-326955 (Claims) 特開平9−150417号公報(特許請求の範囲)JP-A-9-150417 (Claims) 特開2000−288422号公報(特許請求の範囲)JP 2000-288422 A (Claims)

本発明は、上記のような従来技術の課題を背景になされたもので、その目的は、主としてポリプロピレン及び/又はポリエチレン、ポリスチレン、ポリエステルから構成されるペットボトル屑を対象とし、高純度のポリエステル成分を高回収率で分別回収すると同時にポリスチレン成分、ポリエステル成分をほとんど含まないポリプロピレン及び/又はポリエチレンを分別し、分離性能を維持したまま大規模処理することができる廃プラスチックスの分別方法を提供することにある。   The present invention has been made against the background of the problems of the prior art as described above, and its purpose is mainly directed to PET bottle scraps composed of polypropylene and / or polyethylene, polystyrene, and polyester, and a high-purity polyester component. A method of separating waste plastics that can be separated and collected at a high recovery rate, and at the same time, separates polypropylene and / or polyethylene containing almost no polyester component and polyester component, and can be processed on a large scale while maintaining separation performance. It is in.

本発明者らは、上記した従来技術に鑑み、鋭意検討を重ねた結果、予め破砕された廃棄プラスチックから特定比重のプラスチックを回収する方法であって、下記(a)〜(c)の工程を持つ分別装置を用いて分離することを特徴とする廃棄プラスチックの分離方法を用いることによりポリプロピレン及び/又はポリプロピレン、ポリスチレン、及び、ポリエステルを含むペットボトル屑から高純度のポリエステルとポリプロピレン及び/又はポリプロピレンを高回収率で分別する方法を完成するに至った。
(a)破砕された廃棄プラスチック及び水の供給口を有し、攪拌槽内にて破砕された廃棄プラスチックを水と混合し水スラリーをなし、廃棄プラスチックに付着する気泡を分離させ、搬送設備にて廃棄プラスチックの水スラリーを工程(b)に搬送する工程
(b)下部コーン角度が40度以下である下部コーン型円筒攪拌槽とその下に連結管を介して貯槽を有し、更に貯槽内部の充填物を外部に取り出すための搬送設備を有する装置に対し、工程(a)の廃棄プラスチックの水スラリーを下部コーン型円筒攪拌槽内に旋回流が生じるように下部コーン型円筒攪拌槽の直胴部接線方向に設置された水スラリー供給口より供給し、下部コーン型円筒攪拌槽内部を水が旋回しながら上昇速度7〜40mm/秒の上昇する流れにより水スラリー中の低比重プラスチックを、下部コーン型円筒攪拌槽上部に水スラリー供給口からの高さが下部コーン型円筒攪拌槽径の0.5〜5.0倍上方になるように設置されたオーバーフロー口より水と共に排出すると同時に、水スラリー中の高比重プラスチックを下部コーン型円筒攪拌槽下部を経由して貯槽下部より搬送設備を用いて排出し、更に排出された高比重プラスチックと水を脱水装置で分離する工程
(c)分離された低比重プラスチックの水スラリーを遠心分離機に供給し、水より高比重の成分を固形分として排出し、水以下の低比重の成分を水と共に排出し、更に排出されたプラスチックと水を脱水装置で分離する工程
As a result of intensive studies in view of the above-described conventional technology, the present inventors are a method of recovering a plastic having a specific gravity from waste plastic that has been crushed in advance, and include the following steps (a) to (c): High-purity polyester and polypropylene and / or polypropylene from plastic bottle waste containing polypropylene and / or polypropylene, polystyrene, and polyester by using a separation method of waste plastic characterized by separating using a separation device The method of sorting at a high recovery rate has been completed.
(A) It has a supply port for crushed waste plastic and water, mixes the crushed waste plastic in the stirring tank with water to form a water slurry, separates bubbles adhering to the waste plastic, A step (b) for transporting the waste plastic water slurry to the step (b), a lower cone type cylindrical stirring tank having a lower cone part angle of 40 degrees or less, and a storage tank provided thereunder via a connecting pipe; For an apparatus having a transportation facility for taking out the internal packing to the outside, the waste plastic water slurry of step (a) is placed in the lower cone type cylindrical stirring tank so that a swirling flow is generated in the lower cone type cylindrical stirring tank. The water slurry is supplied from the water slurry supply port installed in the tangential direction of the straight body portion, and the water in the water slurry is caused by the rising speed of 7 to 40 mm / second while the water swirls inside the lower cone type cylindrical stirring tank. The specific gravity plastic is put together with water from the overflow port installed at the upper part of the lower cone type cylindrical stirring tank so that the height from the water slurry supply port is 0.5 to 5.0 times the diameter of the lower cone type cylindrical stirring tank. At the same time of discharging, the process of discharging the high specific gravity plastic in the water slurry from the lower part of the storage tank through the lower cone type cylindrical stirring tank using a transport facility, and further separating the discharged high specific gravity plastic and water with a dehydrator (C) The separated water slurry of the low specific gravity plastic is supplied to the centrifuge, the components having a higher specific gravity than water are discharged as solids, the components having a lower specific gravity than water are discharged together with the water, and further discharged. The process of separating plastic and water with a dehydrator

以上に説明した分離装置を用いた廃プラスチック分別方法を使用することによりポリプロピレン及び/又はポリプロピレン、ポリスチレン、及び、ポリエステルを含むペットボトル屑から高純度のポリエステルとポリプロピレン及び/又はポリプロピレンを高回収率で分別することができ、極めて有用である。   By using the waste plastic separation method using the separation apparatus described above, high purity polyester and polypropylene and / or polypropylene can be recovered from polypropylene bottles and / or polypropylene, polystyrene, and PET bottle waste containing polyester with high recovery rate. It can be separated and is extremely useful.

以下、本発明の実施の形態について、廃棄プラスチックが主にポリエチレンテレフタレートからなるボトル(ペットボトル)である場合を図を用いて詳細に説明する。これは本発明の好ましい一形態ではあるが、廃棄プラスチックがペットボトルである場合や図1と全く同じ設備を用いた場合に限定されるものではない。   Hereinafter, the embodiment of the present invention will be described in detail with reference to the drawings when the waste plastic is a bottle (pet bottle) mainly made of polyethylene terephthalate. Although this is a preferred embodiment of the present invention, the present invention is not limited to the case where the waste plastic is a plastic bottle or the same equipment as in FIG.

予め破砕機などにより破砕されたポリプロピレン及び/又はポリプロピレン1a、ポリスチレン1b及びポリエステル1cから構成される廃ペットボトル1は廃ペットボトル投入口5から、また、水2は水供給口7からそれぞれ混合槽4に投入される。次にNo.1攪拌機6により混合されながら均一水スラリーとなり、廃ペットボトル表面に付着する気泡が除去される。この際、廃ペットボトルの水スラリー中の濃度は供給量を調整することで任意選ぶことができるが、水スラリー濃度が高くなると均一混合が困難なる他、廃ペットボトル小片の表面に付着する気泡を除去する目的を果すには10重量%以下であることが好ましい。また、廃ペットボトルの破砕の大きさは特に限定されるものではないが、破砕面が増加することにより破砕面の毛羽立ちなどによる絡まりが多くなる為、8mm〜20mm程度が最も好ましい。更に、攪拌は気泡を除去する目的を果すに十分であり、水スラリーを均一に混合できる強さであればよく、攪拌翼としてはパドル翼、タービン翼など通常使用されるすべての攪拌翼が使用できる。   Waste PET bottles 1 made of polypropylene and / or polypropylene 1a, polystyrene 1b and polyester 1c previously crushed by a crusher or the like are mixed from the waste PET bottle inlet 5 and water 2 is mixed from the water supply port 7 respectively. 4 is input. Next, while mixing by No. 1 stirrer 6, it becomes a uniform water slurry, and bubbles adhering to the surface of the waste PET bottle are removed. At this time, the concentration of the waste PET bottle in the water slurry can be arbitrarily selected by adjusting the supply amount, but if the water slurry concentration becomes high, uniform mixing becomes difficult, and bubbles adhering to the surface of the waste PET bottle small piece In order to achieve the purpose of removing the content, it is preferably 10% by weight or less. Further, the size of the waste PET bottle crushing is not particularly limited, but is preferably about 8 mm to 20 mm, because the crushing surface increases and the crushing surface is entangled with fluffing. Furthermore, stirring is sufficient to achieve the purpose of removing bubbles, and it is sufficient if the water slurry can be mixed uniformly. As stirring blades, all commonly used stirring blades such as paddle blades and turbine blades are used. it can.

混合された廃プラスチック水スラリーはNo.1 スラリーポンプ8により下部コーン型円筒攪拌槽9の直胴部に接線方向に設置された廃ペットボトル水スラリー供給口11から槽内部で旋回流を形成するように供給される。供給された水スラリー中の廃ペットボトルは旋回しながらNo.2 攪拌機10による攪拌効果で小片の重なりなど解除されることにより高比重プラスチックであるポリエステル成分が沈降し、連結管13を経て高比重成分沈降槽(貯槽)14に落下する。下部コーン型円筒攪拌槽の下部コーンの角度は40度を越える場合にはポリエステル成分の高比重成分沈降槽14への落下が遅く、連結管上部にてポリエステル小片が閉塞する可能性があるので、下部コーン角度は40度以下とすることが好ましい。30度以下がより好ましいまた供給された水は全量旋回しながら上昇流れを形成し、オーバーフロー口12より排出される。比重が1より小さいポリプロピレン及び/又はポリエチレンは攪拌効果によりポリエステル成分に同伴されることなく完全に水の流れに伴ってオーバーフロー口12から取り出される。また、ポリエステルよりは比重が小さいものの、比重が1よりも大きなポリスチレン1bを主成分とするペットボトルのラベル等は供給された水の上昇流れを7mm/秒以上とすることにより沈降速度より水の上昇流れが強くなりポリエステル側に混入することなく水流れと共にオーバーフロー口12から取り出される。逆に水の上昇流れが40mm/秒を超えるとするとポリエステル成分もポリスチレンと同様に水流れによりオーバーフロー口側に混入し始める為、高比重成分としてのポリエステル回収率が低下する。そのため、水の上昇流れは7mm/秒〜40mm/秒の範囲とすることが重要である。更に好ましくは10mm/秒〜20mm/秒とすることで安定した高分別能力を維持することができる。廃ペットボトル水スラリー供給口11とオーバーフロー口12の間にて水の上昇流によりオーバーフロー口側に持ち込まれる廃プラスチックを精密分離している。この距離が短い場合には分離時間がとれずポリエステル成分のオーバーフロー口側への混入割合が増加し、長い場合には下部コーン型円筒攪拌槽の装置サイズが大きくなる他、ポリスチレン成分が装置内に滞留するなどの問題が発生する可能性があるため、廃ペットボトル水スラリー供給口11とオーバーフロー口12までの垂直距離は下部コーン型円筒攪拌槽径の0.5倍〜5倍にする必要があり、更に好ましくは下部コーン型円筒攪拌槽径と1.0倍〜2倍とすることで高分離性能を達成することができる。 The mixed waste plastic water slurry forms a swirl flow inside the tank from the waste PET bottle water slurry supply port 11 tangentially installed in the straight body of the lower cone type cylindrical stirring tank 9 by the No. 1 slurry pump 8. Supplied as The waste plastic bottle in the supplied water slurry turns while turning. 2 The polyester component, which is a high specific gravity plastic, is settled by releasing the overlapping of small pieces by the stirring effect by the stirrer 10, and falls into the high specific gravity component sedimentation tank (storage tank) 14 through the connecting pipe 13. When the angle of the lower cone of the lower cone type cylindrical stirring tank exceeds 40 degrees, the polyester component is slow to fall into the high specific gravity component settling tank 14, and the polyester piece may be blocked at the upper part of the connecting pipe. The lower cone part angle is preferably 40 degrees or less. The supplied water is more preferably 30 degrees or less, and the supplied water forms a rising flow while swirling the whole amount and is discharged from the overflow port 12. Polypropylene and / or polyethylene having a specific gravity of less than 1 is taken out from the overflow port 12 along with the flow of water without being accompanied by the polyester component due to the stirring effect. Moreover, although the specific gravity is smaller than that of polyester, the label of a PET bottle mainly composed of polystyrene 1b having a specific gravity greater than 1 has a water flow higher than the sedimentation speed by setting the rising flow of the supplied water to 7 mm / second or more. The ascending flow becomes stronger and is taken out from the overflow port 12 together with the water flow without being mixed into the polyester side. On the other hand, if the upward flow of water exceeds 40 mm / second, the polyester component begins to be mixed into the overflow port side by the water flow as in the case of polystyrene, so that the polyester recovery rate as a high specific gravity component decreases. Therefore, it is important that the upward flow of water is in the range of 7 mm / second to 40 mm / second. More preferably, the stable high separation ability can be maintained by setting the speed to 10 mm / second to 20 mm / second. Waste plastic brought into the overflow port side is precisely separated by the upward flow of water between the waste plastic bottle water slurry supply port 11 and the overflow port 12. When this distance is short, the separation time cannot be taken and the mixing ratio of the polyester component to the overflow port side increases, and when it is long, the apparatus size of the lower cone type cylindrical stirring tank increases, and the polystyrene component enters the apparatus. Since a problem such as stagnation may occur, the vertical distance between the waste PET bottle water slurry supply port 11 and the overflow port 12 must be 0.5 to 5 times the diameter of the lower cone type cylindrical stirring tank. More preferably, high separation performance can be achieved by adjusting the diameter of the lower cone type cylindrical stirring tank to 1.0 to 2 times.

ポリエステル成分1cは高比重成分沈降槽14からスクリューコンベアー15により水面上まで搬送され、高比重成分排出口16からNo.1 脱水機17で脱水されて回収される。一方、オーバーフロー口12から取り出されるポリプロピレン及び/又はポリエチレン、ポリスチレンの水スラリーはNo.2 スラリーポンプ18により遠心分離機19に供給され、ケーク排出口20側よりポリスチレン成分1bが回収される。また、同時にろ液排出口21より水と共に排出されるポリプロピレン及び/又はポリエチレン成分1cはNo.2 脱水機22で脱水され、回収される。No.1及びNo.2脱水機、No.1及びNo.2スラリーポンプ、遠心分離機などの機械設備についてはタイプなど特段限定されるものではなく、汎用機械を使用することができる。本設備を使用することにより回収されるポリエステル成分は純度99.8%以上、回収率99%以上を達成可能であり、同時にポリプロピレン及び/又はポリエチレンは純度、回収率共に99.5%以上を達成することが可能であり、更に数トン/時以上の廃プラスチック処理が可能な上、処理量低下時も水スラリー濃度の調整などにより分別能力の低下が防止でき優れた分別方法である。   The polyester component 1c is conveyed from the high specific gravity component sedimentation tank 14 to the surface of the water by the screw conveyor 15, and is dehydrated and recovered by the No. 1 dehydrator 17 from the high specific gravity component discharge port 16. On the other hand, an aqueous slurry of polypropylene and / or polyethylene and polystyrene taken out from the overflow port 12 is supplied to the centrifuge 19 by a No. 2 slurry pump 18 and the polystyrene component 1b is recovered from the cake discharge port 20 side. At the same time, the polypropylene and / or polyethylene component 1c discharged together with water from the filtrate outlet 21 is No. 2 Dehydrated by the dehydrator 22 and collected. The machine equipment such as No. 1 and No. 2 dehydrators, No. 1 and No. 2 slurry pumps, centrifuges and the like are not particularly limited, such as type, and general-purpose machines can be used. Polyester components recovered by using this equipment can achieve a purity of 99.8% or more and a recovery rate of 99% or more. At the same time, polypropylene and / or polyethylene achieve a purity and recovery rate of 99.5% or more. In addition, waste plastic processing of several tons / hour or more is possible, and even when the processing amount is reduced, the separation ability can be prevented from being lowered by adjusting the concentration of the water slurry.

以下実施例により本発明の内容をさらに具体的に説明するが本発明はこれにより何等限定を受けるものではない。回収率については下式に基づき算出した。
回収率=各箇所に分別されたプラスチック重量×対象成分の純度/原料廃プラスチック中の対象成分重量
The contents of the present invention will be described more specifically with reference to the following examples, but the present invention is not limited thereto. The recovery rate was calculated based on the following formula.
Recovery rate = plastic weight sorted at each location x purity of the target component / target component weight in the waste plastic

[実施例1]
図1の設備にて廃ペットボトルを12mmサイズに破砕したものを用いて実施した。分別実験において下部コーン型円筒攪拌槽内の水上昇流を10mm/秒となるように水スラリー濃度を調整し、この間に破砕物に付着していた気泡を取り除いた。また、下部コーン型円筒攪拌槽のフィード位置からオーバーフロー位置までの距離を槽径とあわせ、コーン角度30度の装置で廃ペットボトル1000kg/時で処理した結果を下表の実施例1に示す。
[Example 1]
The waste PET bottle was crushed into a 12 mm size using the equipment shown in FIG. In the fractionation experiment, the water slurry concentration was adjusted so that the upward flow of water in the lower cone type cylindrical stirring tank was 10 mm / second, and bubbles adhering to the crushed material were removed during this time. Also shows together a distance to the overflow position with So径from the feed position of the lower cone type cylindrical stirring vessel, a result of processing when waste PET bottles 1000 kg / in device cone angle of 30 degrees to the first embodiment in the following table .

[実施例2〜3、比較例1〜3]
実施例2〜3、比較例1〜3については水上昇流の値と、下部コーン型円筒攪拌槽のフィード位置からオーバーフロー位置までの高さを変更して実施した。その結果の詳細を表1にまとめた。比較項目は各々分別品の純度と回収率である。
[Examples 2-3, Comparative Examples 1-3]
Examples 2 to 3 and Comparative Examples 1 to 3 were carried out by changing the value of the water upward flow and the height from the feed position to the overflow position of the lower cone type cylindrical stirring tank. Details of the results are summarized in Table 1. The comparison items are the purity and recovery rate of each fraction.

[比較例4]
下部コーン型円筒攪拌槽のコーン角度を45度の装置とした以外は実施例1と同一条件で分別試験を実施した結果、下部コーン型円筒混合槽内コーン部にて高比重成分であるポリエステルが閉塞し、分別テストを継続できなくなった。
[Comparative Example 4]
Except that the cone portion angle of the lower cone type cylindrical stirring tank 45 degrees devices result of the fractionation test under the same conditions as in Example 1, a polyester is a high density component at a lower cone type cylindrical mixing chamber cone section Was blocked and could not continue the separation test.

Figure 0004804115
Figure 0004804115

実施例1〜3、比較例1〜3にて表されているように、以上に説明した分離装置を用いた廃プラスチック分別方法を使用することによりポリプロピレン及び/又はポリプロピレン、ポリスチレン、及び、ポリエステルを含むペットボトル屑から高純度のポリエステルとポリプロピレン及び/又はポリプロピレンを高回収率で分別することができる。ゆえにそれぞれのプラスチックのリサイクルが効率的に実施することができ、極めて有用である。 As shown in Examples 1 to 3 and Comparative Examples 1 to 3, polypropylene and / or polypropylene, polystyrene, and polyester can be obtained by using the waste plastic separation method using the separation apparatus described above. High-purity polyester and polypropylene and / or polypropylene can be separated from the plastic bottle scraps contained at a high recovery rate. Therefore, recycling of each plastic can be carried out efficiently and is extremely useful.

本発明における工程(a)の実施の一態様を示した概略図である。It is the schematic which showed the one aspect | mode of implementation of the process (a) in this invention.

1・・・廃ペットボトル
1a・・ポリプロピレン及び/又はポリエチレン成分
1b・・ポリスチレン成分
1c・・ポリエステル成分
2・・・水
3・・・排水
4・・・混合槽
5・・・廃ペットボトル投入口
6・・・No.1攪拌機
7・・・水供給口
8・・・No.1スラリーポンプ
9・・・下部コーン型円筒攪拌槽
10・・・No.2攪拌機
11・・・廃ペットボトル水スラリー供給口
12・・・オーバーフロー口
13・・・連結管
14・・・高比重成分沈降槽
15・・・スクリューコンベアー
16・・・高比重成分排出口
17・・・No.1脱水機
18・・・No.2スラリーポンプ
19・・・遠心分離機
20・・・ケーク排出口
21・・・ろ液排出口
22・・・No.2脱水機
DESCRIPTION OF SYMBOLS 1 ... Waste PET bottle 1a ... Polypropylene and / or polyethylene component 1b ... Polystyrene component 1c ... Polyester component 2 ... Water 3 ... Drainage 4 ... Mixing tank 5 ... Waste plastic bottle input Mouth 6 ... No. 1 Stirrer 7 ... Water supply port 8 ... No. 1 Slurry pump 9... Lower cone type cylindrical stirring tank 10. 2 Stirrer 11 ... Waste PET bottle water slurry supply port 12 ... Overflow port 13 ... Connecting pipe 14 ... High specific gravity component sedimentation tank 15 ... Screw conveyor 16 ... High specific gravity component discharge port 17 ... No. 1 Dehydrator 18 ... No. 2 Slurry pump 19 ... Centrifuge 20 ... Cake outlet 21 ... Filtrate outlet 22 ... No. 2 dehydrator

Claims (5)

予め破砕された廃棄プラスチックから特定比重のプラスチックを回収する方法であって、下記(a)〜(c)の工程を持つ分別装置を用いて分離することを特徴とする廃棄プラスチックの分離方法。
(a)破砕された廃棄プラスチック及び水の供給口を有し、攪拌槽内にて破砕された廃棄プラスチックを水と混合し水スラリーをなし、廃棄プラスチックに付着する気泡を分離させ、搬送設備にて廃棄プラスチックの水スラリーを工程(b)に搬送する工程
(b)下部コーン角度が40度以下である下部コーン型円筒攪拌槽とその下に連結管を介して貯槽を有し、更に貯槽内部の充填物を外部に取り出すための搬送設備を有する装置に対し、工程(a)の廃棄プラスチックの水スラリーを下部コーン型円筒攪拌槽内に旋回流が生じるように下部コーン型円筒攪拌槽の直胴部接線方向に設置された水スラリー供給口より供給し、下部コーン型円筒攪拌槽内部を水が旋回しながら上昇速度7〜40mm/秒の上昇する流れにより水スラリー中の低比重プラスチックを、下部コーン型円筒攪拌槽上部に水スラリー供給口からの高さが下部コーン型円筒攪拌槽径の0.5〜5.0倍上方になるように設置されたオーバーフロー口より水と共に排出すると同時に、水スラリー中の高比重プラスチックを下部コーン型円筒攪拌槽下部を経由して貯槽下部より搬送設備を用いて排出し、更に排出された高比重プラスチックと水を脱水装置で分離する工程
(c)分離された低比重プラスチックの水スラリーを遠心分離機に供給し、水より高比重の成分を固形分として排出し、水以下の低比重の成分を水と共に排出し、更に排出されたプラスチックと水を脱水装置で分離する工程
A method for recovering a plastic having a specific gravity from waste plastic that has been crushed in advance, wherein the plastic is separated using a sorting apparatus having the following steps (a) to (c).
(A) It has a supply port for crushed waste plastic and water, mixes the crushed waste plastic in the stirring tank with water to form a water slurry, separates bubbles adhering to the waste plastic, A step (b) for transporting the waste plastic water slurry to the step (b), a lower cone type cylindrical stirring tank having a lower cone part angle of 40 degrees or less, and a storage tank provided thereunder via a connecting pipe; For an apparatus having a transportation facility for taking out the internal packing to the outside, the waste plastic water slurry of step (a) is placed in the lower cone type cylindrical stirring tank so that a swirling flow is generated in the lower cone type cylindrical stirring tank. The water slurry is supplied from the water slurry supply port installed in the tangential direction of the straight body portion, and the water in the water slurry is caused by the rising speed of 7 to 40 mm / second while the water swirls inside the lower cone type cylindrical stirring tank. The specific gravity plastic is put together with water from the overflow port installed at the upper part of the lower cone type cylindrical stirring tank so that the height from the water slurry supply port is 0.5 to 5.0 times the diameter of the lower cone type cylindrical stirring tank. At the same time of discharging, the process of discharging the high specific gravity plastic in the water slurry from the lower part of the storage tank through the lower cone type cylindrical stirring tank using a transport facility, and further separating the discharged high specific gravity plastic and water with a dehydrator (C) The separated water slurry of the low specific gravity plastic is supplied to the centrifuge, the components having a higher specific gravity than water are discharged as solids, the components having a lower specific gravity than water are discharged together with the water, and further discharged. The process of separating plastic and water with a dehydrator
工程(b)における円筒攪拌槽内部を水が旋回しながら上昇する流れの上昇速度が10mm/秒〜20mm/秒であることを特徴とする請求項1記載の廃棄プラスチックの分離方法。   2. The method for separating waste plastics according to claim 1, wherein the rising speed of the flow of water rising while swirling inside the cylindrical stirring tank in the step (b) is 10 mm / second to 20 mm / second. 工程(b)における下部コーン型円筒攪拌槽において廃棄プラスチックの水スラリーの供給口からオーバーフロー口までの垂直距離が、下部コーン型円筒攪拌槽径の1.0倍〜2.0倍の範囲であることを特徴とする請求項1記載の廃棄プラスチックの分離方法。   In the lower cone type cylindrical stirring tank in the step (b), the vertical distance from the waste plastic water slurry supply port to the overflow port is in the range of 1.0 to 2.0 times the diameter of the lower cone type cylindrical stirring tank. The method for separating waste plastics according to claim 1. 予め破砕された廃棄プラスチックが主にポリエチレンテレフタレートからなるボトルであることを特徴とする請求項1記載の廃棄プラスチックの分離方法。   2. The method for separating waste plastic according to claim 1, wherein the waste plastic crushed in advance is a bottle mainly composed of polyethylene terephthalate. 工程(b)における下部コーン型円筒攪拌槽において下部コーン角度が30度以下であることを特徴とする請求項1記載の廃棄プラスチックの分離方法。 The method for separating plastic waste according to claim 1, wherein the lower cone portion angle in the lower cone type cylindrical stirring tank in step (b) is 30 degrees or less.
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